Investigating pyrolysis characteristics of dendrocalamus asper bamboo

Chia sẻ: Nguyễn Thảo | Ngày: | Loại File: PDF | Số trang:9

Thêm vào BST

Báo xấu

12
lượt xem 1
download

Download Vui lòng tải xuống để xem tài liệu đầy đủ

Green engineering investigated as a possible organic green material in the combustion process and heating applications. A bioreactor system processed Dendrocalamus asper bamboo culms as green engineering materials to theto industrial process that produces valuable elements from a natural treatment by soaking with an average of pH 7.6 level of sea-water.

Chủ đề:

Bình luận(0) Đăng nhập để gửi bình luận!

Lưu

Nội dung Text: Investigating pyrolysis characteristics of dendrocalamus asper bamboo

International Journal of Mechanical Engineering and Technology (IJMET) Volume 10, Issue 03, March 2019, pp. 1079-1087. Article ID: IJMET_10_03_109 Available online at http://www.iaeme.com/ijmet/issues.asp?JType=IJMET&VType=10&IType=3 ISSN Print: 0976-6340 and ISSN Online: 0976-6359 © IAEME Publication Scopus Indexed INVESTIGATING PYROLYSIS CHARACTERISTICS OF DENDROCALAMUS ASPER BAMBOO *Teodoro A. Amatosa, Jr. Engineering Graduate Program, School of Engineering, University of San Carlos, Talamban Campus, Cebu City, 6000 Philippines Michael E. Loretero Department of Mechanical and Manufacturing Engineering, University of San Carlos, Talamban Campus, Cebu City, 6000 Philippines Yee-wen Yen Department of Materials Science and Engineering, National Taiwan University of Science and Technology, Taipei 106, Taiwan Andromeda Dwi Laksono Institut Teknologi Kalimantan, Kampus ITK Karang Joang, Balikpapan 76127, Kalimantan Timur, Indonesia. *Corresponding Author ABSTRACT Green engineering investigated as a possible organic green material in the combustion process and heating applications. A bioreactor system processed Dendrocalamus asper bamboo culms as green engineering materials to theto industrial process that produces valuable elements from a natural treatment by soaking with an average of pH 7.6 level of sea-water. Pyrolysis Combustion Flow Calorimeter and Differential Scanning Calorimetry (DSC) to utilized the precise heat capacity extent to characterize the materials. A waste product in this process is the activated carbon, which is highly in demand for water cleansing system and sold to neutralize the fuel cost. The primary stage at 68-89oC is the exothermic dehydration of the biomass with the release of water and low-molecular-weight gases like carbon monoxide (CO) and carbon dioxide (CO2). The results from this research will be significant and helpful to develop and utilize the wastes from Dendrocalamus asper bamboo with 134.58 kJ for any renewable energy product. Keywords: natural treatment, pyrolysis, green engineering, biomass. http://www.iaeme.com/IJMET/index.asp 1079 editor@iaeme.com
Teodoro A. Amatosa, Jr., Michael E. Loretero, Yee-wen Yen and Andromeda Dwi Laksono Cite this Article: Teodoro A. Amatosa, Jr., Michael E. Loretero, Yee-wen Yen and Andromeda Dwi Laksono, Investigating Pyrolysis Characteristics of Dendrocalamus Asper Bamboo, International Journal of Mechanical Engineering and Technology, 10(3), 2019, pp. 1079-1087. http://www.iaeme.com/IJMET/issues.asp?JType=IJMET&VType=10&IType=3 1. INTRODUCTION Through pyrolysis technology, biomass could turn into chemicals with high value and with energy-density products such as liquid, solid-state energy, and gas. Evaluation of bamboo through life cycle assessment is presented to resolve the environmental implication of bamboo as a source for construction material. The results of this interpretation show that, in some applications, bamboo has marked by a high "factor 20" environmental impact, a 20 times less load on the environment than compared to some alternatives [1]. Wood and bamboo have renown in the green engineering technology industry recently because of their environmentally promising characteristics: a natural process can replace them, biodegradable, confine carbon from the atmosphere, low in combined energy, and providing less pollution in development than concrete or steel [2, 3]. One of the priority products during slow pyrolysis is the biochar, which can utilize as solid fuels [4], soil amendment [5], activated carbon precursor [6], metallurgical industry reduction [7] and material for absorption in environmental cleanup and wastewater treatment [8, 9]. Its properties are widely affected by pyrolysis set-up such as feedstock type, pyrolysis temperature, ash composition, inert or low oxygen environment, heating rate, and pretreatment methods [10, 11]. Materials for feedstock pyrolysis such as wood is one of the renewable biomass been use [12], coconut husk [13], corn stover [14], bamboo [15], and microalgae [16]. Fast growth, shorter felling period (3–5 years) and lower ash content are bamboos advantage. Cellulose, hemicellulose, and lignin are primary components of the bamboo that can utilize for the production of various chemicals with high value-added [17, 18]. Based on the past few years of the increased production, the advantages of high porous structure and large surface area are from bamboo-derived biochar. The influence of reaction conditions during the process which the researchers give interest in the kinds of biomass for pyrolyzing, properties and its application from different types of biochar. Rice straw as materials from agricultural waste [19], peanut hull [20], and crop residue [21], palm kernel shell from forestry waste [22], hardwood sawdust [23] and pine needles [24], and some sewage sludge from garbage [25] and chicken manures [26]. In terms of reaction conditions, much research had done before. [27] Investigated and found that the biochar yield particle size increased and the effect of temperature through pyrolysis was decreasing or with increasing the sample particle size. The investigated reaction time and biomass pyrolysis, [22] used the microwave to analyze the flow rate of nitrogen gas of sample mass and to determine the optimum pyrolysis condition. Besides that, [28] investigated the heating rate data on biochar production from 1 and 100 ◦C. To be precise, the concentration of stable C in biochar through heating rate had an outstanding impact. [21] Found that high-temperature biochar produced had higher surface area; lower organic and with low temperature and higher oxygen content. And lastly, biochar always used for countering land degradation and improving agriculture [29], and adsorption of heavy metal ions [30]. In this study, pyrolysis of bamboo (Dendrocalamus asper) was conducted at fixed bed pyrolysis locally manufactured reactor to establish pyrolysis as feedstock product yield data (especially for biochar) and energy transfer of cooling air during slow pyrolysis. The transformation of native bamboo by pyrolysis to biochar can be a potential and alternative option for industries of steel making, soil amelioration, carbon sequestration, wastewater http://www.iaeme.com/IJMET/index.asp 1080 editor@iaeme.com
Investigating Pyrolysis Characteristics of Dendrocalamus Asper Bamboo treatment and so on. These results will provide necessary information for bamboo pyrolysis to consider the parameter optimization and large-scale pyrolysis system development. 2. MATERIALS AND METHODS 2.1. Materials Three-year-old Giant Bamboo (Dendrocalamus asper) harvested from Mandaue City, Province of Cebu in the Philippines. Portions cut up to 3.0 m from the basal part that will use for the assessment. The bamboo was manually cut into a specified length of 300 mm and was split longitudinally at the top, middle and bottom part of the bamboo. A set up was performed using traditional treatment by soaking it in sea-water and show up the specimens to wetting and drying cycle; the bamboo specimens were removed from the water and were stacked vertically in air- drying for one (1) week [31]. Table 1 Macroscopic characteristics of Giant bamboo (Dendrocalamus asper) Macroscopic Characteristics Unit [32] Literature [33] [34] Philippine Bamboo * Culm length M 20-30 18-23 - 20-30 Internode length Cm 20-25 35 14-45 30-35 Internode Diameter cm 8-20 9-13 1.2-9.3 8-18 Culm wall Thickness Mm 11-20 10-14 4-30 6-13 *Present study 32 Dransfield and Widjaja. 1995. 33 Othman et al. 1995. 34 Pakhkeree. 1997. 2.2. Methods The external heat source made from electric resistance and heating element used was nichrome wire. Nichrome made from nickel, often iron, and chromium. To produce enough resistance and generate heat, any conductive wire and some metals can be utilized for heating that has great efficiency to conduct electricity. Once heated, nichrome wire could not be compared to some metals that oxidize quickly and become brittle and break when heated in the air due to its outer layer with chromium oxide, mostly impenetrable to oxygen, relation to energy and work are stable in air and prevent for further oxidation through the heating element. The reactor design presented in the figures was manufacture by Ralds Corporation located at Kagudoy Road, Talamban, Cebu. The experimental set-up operated at a maximum temperature of 340°C and heating rate of 3°C /min. http://www.iaeme.com/IJMET/index.asp 1081 editor@iaeme.com
Teodoro A. Amatosa, Jr., Michael E. Loretero, Yee-wen Yen and Andromeda Dwi Laksono Figure 1 shows the photograph of the experimental setup (a) reactor; (b) set-up for data gathering; and (c) temperature and weight gathering set-up 3. RESULTS AND DISCUSSION This paper analyzed the treated Giant bamboo species within one week and air-dried for another week the possibility of energy utilization through pyrolysis. Figure 2 curves of Philippine bamboo in temperature vs. time vs. mass loss http://www.iaeme.com/IJMET/index.asp 1082 editor@iaeme.com
Investigating Pyrolysis Characteristics of Dendrocalamus Asper Bamboo The significant mass loss was noticed in figure 2 at around 300°C — the same as the work of [35] on pyrolysis. This stage, according to them, is attributed primarily to the decomposition into volatiles. Moreover, the mass loss at 20-280°C was mostly due to the successive evaporation of the volatile hydrocarbon and the low-molecular-weight hydrocarbons at 280- 400°C; 400 and 500°C mass loss due to a composition of thermal cracking and medium- molecular-weight hydrocarbons [36]. Figure 3 shows the graphical data analysis (a) temperature history of the gas vs. temperature rise and, (b) gas and air data vs. time Table 2 Specific Data for Energy Transfer 3.1. Analysis of Gases on Condenser Side The pyrolysis procedure can be divided, from a thermal standpoint, into stages, according to [37]. At the drying stage (~100°C), free moisture and some unbound water released. These explain the discovery of temperature due to the available moisture released by the feedstock (Dendrocalamus asper). The initial stage at 100-300°C is the exothermic dehydration of the biomass to allow water and early-molecular-weight gases like CO and CO2. The intermediate stage which occurs at 200-600°C is the primary pyrolysis where most of the vapor or precursor to bio-oil produced. These explain the continued rise of the temperature because of the presence of gases aside from the moisture. Moreover, from the work of [38] on pyrolysis of coconut biomass, CO2 was produced as the temperature reached 150°C. The formation of CO, CH4, and H2 followed that of CO2 as the temperature continued to increase. The composition of CO2 and CO reached the maximum at a temperature equal to 300°C. It has explained that the pyrolysis of cellulose produces between 300 and 400°C of CO2 and CO [39]. The same form of the graph has observed in the work of [35] on pyrolysis. The temperature fluctuation of the sensors might explain by the complex flow developed in the pipeline, which was caused by the conversion of the feedstock into oil and gas generating in the pipeline. http://www.iaeme.com/IJMET/index.asp 1083 editor@iaeme.com
Teodoro A. Amatosa, Jr., Michael E. Loretero, Yee-wen Yen and Andromeda Dwi Laksono Figure 4 DSC curves of Philippine bamboo (Dendrocalamus asper) on (a) bottom, (b) middle, and (c) top part Analysis using Differential scanning calorimetry (DSC) performed on the different portions (bottom, middle and top) of giant bamboo are shown in Figures 4a, 4b, and 4c. The graphs in Figure 4, an endothermic and exothermic event for giant bamboo fiber is observable in the all position — these events displayed through a result of exothermic and endothermic peaks. For the examined giant bamboo, parts have broad endothermic peaks could be observed in the temperature range of 30 to 135°C. Negative displacement occurred when heat concentration by the bamboo fibers direct to the evaporation of free water position within cellulose. The transition temperature of unbound or open water in a natural mixture of the compound is the same measurement to pure water, while it is higher than bound water [40]. From Fig. 4, it can notice that in the endotherm, the endothermic peak of bottom giant bamboo fig. 2a (89 °C) is the highest and that of bottom giant bamboo fig.4c (68 °C) is the lowest similar to others. Thus, bottom giant bamboo number 3 probably has the highest lignocellulose content which means endothermic reactions indicated that the depolymerization of cellulose molecules of bamboo required higher temperatures due to their higher stabilities. The endothermic peak of bottom giant bamboo fig. 4a has a higher temperature of 82.82°C compared with [41]. The observation involved bottom giant bamboo figures 4a, 4b and 4c portions that exhibited an exothermic peak at 330, 334, and 330 °C, respectively, which was indicative of the charging process and resulted in little residual material. The exothermic events in these parts might connect to breakage of cellulose chains in a crystalline region (highly ordered) of their microfibrils [39]. 4. CONCLUSION A native organic material from the Philippines has properties showing better performance to some other natural fibers (cellulose, hemp, flax, and sugar cane). Moreover, the temperature is affected by the fluctuation of the gas flow and that a positive relationship characterizes it. From the data, giant bamboo has the exothermic peak in the range 334-341oC and 68-89oC for exothermic dehydration. Temperatures increased as the gas flow increased and rapidly decreased as the flow subsided. In most cases, this char layer leads to reduction because of the limitation of mass and thermal assign. ACKNOWLEDGEMENT This study conceptualized by the author/s and sponsored through Engineering Research and Development for Technology under the Department of Science and Technology, the Philippines and all experiments were carried out in the Department of Mechanical and Manufacturing Engineering Laboratory, University of San Carlos, Cebu City, 6000 Philippines and to Engr. http://www.iaeme.com/IJMET/index.asp 1084 editor@iaeme.com
Investigating Pyrolysis Characteristics of Dendrocalamus Asper Bamboo Andromeda Dwi Laksono and Prof. Dr. Yee-wen Yen for some inputs and allowing the researcher to conduct microstructure experiments and analysis at the Electronic Packaging and Green Materials Laboratory, National Taiwan University of Science and Technology, Taipei 106, Taiwan. REFERENCES [1] Van der Lugt, P., Van den Dobbelsteen, AAJF., and Janssen, JJA. 2006. An environmental, economic, and practical assessment of bamboo as a building material for supporting structures. Constr. Build. Mater, 20(9), 648–656. [2] Falk, B. 2009. Wood as a sustainable building material. Prod. J. 59(9):6e12. [3] Mahdavi, M., Clouston. PL., Arwade, SR. 2011. Development of laminated bamboo lumber: review of processing, performance, and economical considerations. J Mater Civ Eng, 23(7):1036e42. [4] Wang, B., Sun, L., Su, S., Xiang, J., Hu, S., Fei, H., 2012. Char structural evolution during pyrolysis and its influence on combustion reactivity in air and oxy-fuel conditions. Energy Fuel 26, 1565–1574. [5] Doumer, M.E., Arízaga, G.G.C., Silva, D.A.D., Yamamoto, C.I., Novotny, E.H., Santos, J.M., Santos, L.O.D., Wisniewski, A., Andrade, J.B.D., Mangrich, A.S., 2015. Slow pyrolysis of different Brazilian waste biomasses as sources of soil conditioners and energy, and for environmental protection. J. Anal. Appl. Pyrol. 113, 434–443. [6] Li, J., Dai, J., Liu, G., Zhang, H., Gao, Z., Fu, J., He, Y., Huang, Y., 2016. Biochar from microwave pyrolysis of biomass: A review. Biomass Bioenergy 94, 228–244. [7] Suopajärvi, H., Pongrácz, E., Fabritius, T., 2013. The potential of using biomass-based reducing agents in the blast furnace: A review of thermochemical conversion technologies and assessments related to sustainability. Renew. Sust. Energ. Rev. 25, 511–528. [8] Li, Y., Shao, J., Wang, X., Deng, Y., Yang, H., Chen, H., 2014. Characterization of modified biochars derived from bamboo pyrolysis and their utilization for target component (furfural) adsorption. Energy Fuel 28, 5119–5127. [9] Peng, X., Hu, F., Zhang, T., Qiu, F., Dai, H., 2018. Amine-functionalized magnetic bamboo- based activated carbon adsorptive removal of ciprofloxacin and norfloxacin: A batch and fixed-bed column study. Bioresour. Technol. 249, 924–934. [10] Wang, Y., Duan, D., Liu, Y., Ruan, R., Fu, G., Dai, L., Zhou, Y., Yu, Z., Wu, Q., Zeng, Z., 2018. Properties and pyrolysis behavior of moso bamboo sawdust after microwave assisted acid pretreatment. J. Anal. Appl. Pyrol. 129, 86–92. [11] Zeng, K., Yang, Q., Zhang, Y., Mei, Y., Wang, X., Yang, H., Shao, J., Li, J., Chen, H., 2018. Influence of torrefaction with Mg-based additives on the pyrolysis of cotton stalk. Bioresour. Technol. 261, 62–69. [12] Russell, S.H., Turrion-Gomez, J.L., Meredith, W., Langston, P., Snape, C.E., 2017. Increased charcoal yield and production of lighter oils from the slow pyrolysis of biomass. J. Anal. Appl. Pyrol. 124, 536–541. [13] Suman, S., Gautam, S., 2017. Pyrolysis of coconut husk biomass: Analysis of its biochar properties. Energy sources part A-recovery. Util. Environ. Eff. 39, 761–767. [14] Vakalis, S., Heimann, R., Talley, A., Heimann, N., Baratieri, M., 2016. Introduction to frictional pyrolysis (FP) – An alternative method for converting biomass to solid carbonaceous products. Fuel 175, 49–56. [15] Xiong, S., Zhang, S., Wu, Q., Guo, X., Dong, A., Chen, C., 2014. Investigation on cotton stalk and bamboo sawdust carbonization for barbecue charcoal preparation. Bioresour. Technol. 152, 86–92. [16] Grierson, S., Strezov, V., Shah, P., 2011. Properties of oil and char derived from slow pyrolysis of Tetraselmis chui. Bioresour. Technol. 102, 8232–8240. http://www.iaeme.com/IJMET/index.asp 1085 editor@iaeme.com
Teodoro A. Amatosa, Jr., Michael E. Loretero, Yee-wen Yen and Andromeda Dwi Laksono [17] Sharma, R.K., Wooten, J.B., Baliga, V.L., Lin, X.H., Chan, W.G., Hajaligol, M.R., 2004. Characterization of chars from pyrolysis of lignin. Fuel 83, 1469–1482. [18] Yan, K., Jarvis, C., Gu, J., Yan, Y., 2015. Production and catalytic transformation of levulinic acid: A platform for specialty chemicals and fuels. Renew. Sust. Energ. Rev. 51, 986–997. [19] H.P. Liu, L.Y. Zhang, Z.J. Han, B.Y. Xie, S.H. Wu, The effects of leaching methods on the combustion characteristics of rice straw, Biomass Bioenergy 49 (2013) 22–27. [20] J.W. Gaskin, R.A. Speir, K. Harris, K.C. Das, R.D. Lee, L.A. Morris, D.S. Fisher, Effect of peanut hull and pine chip biochar on soil nutrients, corn nutrient status, and yield, Agron. J. 102 (2010) 623–633. [21] Y. Chun, G.G. Sheng, C.T. Chiou, B.S. Xing, Composition and sorptive properties of crop residue-derived chars, Environ. Sci. Technol. 38 (2004) 4649–4655. [22] M.A. Jamaluddin, K. Ismail, M.A.M. Ishak, Z.A. Ghani, M.F. Abdullah, M.T. Safian, S.S. Idris, S. Tahiruddin, M.F.M. Yunus, N.I.N.M. Hakimi, Microwave-assisted pyrolysis of palm kernel shell: optimization using response surface methodology (RSM), Renew. Energy 55 (2013) 357–365. [23] D. Fabbri, C. Torri, K.A. Spokas, Analytical pyrolysis of synthetic chars derived from biomass with potential agronomic application (biochar). Relationships with impacts on microbial carbon dioxide production, J. Anal. Appl. Pyrolysis 93 (2012) 77–84. [24] B.L. Chen, D.D. Zhou, L.Z. Zhu, Transitional adsorption and partition of nonpolar and polar aromatic contaminants by biochars of pine needles with different pyrolytic temperatures, Environ. Sci. Technol. 42 (2008) 5137–5143. [25] E. Agrafioti, G. Bouras, D. Kalderis, E. Diamadopoulos, Biochar production by sewage sludge pyrolysis, J. Anal. Appl. Pyrolysis 101 (2013) 72–78. [26] S.O. Tagoe, T. Horiuchi, T. Matsui, Effects of carbonized and dried chicken manures on the growth, yield, and N content of soybean, Plant Soil 306 (2008) 211–220. [27] A. Demirbas, Effects of temperature and particle size on bio-char yield from pyrolysis of agricultural residues, J. Anal. Appl. Pyrolysis 72 (2004) 243–248. [28] K. Crombie, O. Masek, S.P. Sohi, P. Brownsort, A. Cross, The effect of pyrolysis conditions on biochar stability as determined by three methods, GCB Bioenergy 5 (2013) 122–131. [29] C.J. Barrow, Biochar: potential for countering land degradation and for improving agriculture, Appl. Geogr. 34 (2012) 21–28. [30] A. Stafiej, K. Pyrzynska, Adsorption of heavy metal ions with carbon nanotubes, Sep. Purif. Technol. 58 (2007) 49–52. [31] Amatosa, T. Jr., and Loretero, M. 2017. Axial Tensile Strength Analysis of Naturally Treated Bamboo as Possible Replacement of Steel Reinforcement in the Concrete Beam (December 6, 2017). Papua New Guinea University of Technology, Global Virtual Conference in Civil Engineering (GVCCE) 2016. Available at SSRN: https://ssrn.com/abstract=3083832 [32] Dransfield, S. and Widjaja, E. A. 1995. Plant resources of South-east Asia No. 7: Bamboos. Leiden, Netherlands. [33] Othman, AR., Mohmod, AL., Liese, W. and Haron, N. 1995. Research Pamphlet No. 118: Planting and utilization of bamboo in Peninsular Malaysia. Forest Research Institute Malaysia. Kuala Lumpur, Malaysia. [34] Pakhkeree, T. 1997. Physical and mechanical properties of Dendrocalamus asper Becker. M.S. Thesis, Kasetsart University, Thailand. [35] Sun R Ca. Cereal straw as a resource for sustainable biomaterials and biofuels: chemistry, extractives, lignins, hemicelluloses, and cellulose. Elsevier; 2010. http://www.iaeme.com/IJMET/index.asp 1086 editor@iaeme.com
Investigating Pyrolysis Characteristics of Dendrocalamus Asper Bamboo [36] Ali HM, Siddiqui MH, Al-Whaibi MH, Basalah MO, Sakran AM, El-Zaidy M. 2013. Effect of proline and abscisic acid on the growth and physiological performance of faba bean under water stress. Pak J Bot. 45:933–940. [37] Basu, P. 2013. Biomass Gasification, Pyrolysis, and Torrefaction – 2nd Edition – Elsevier. eBook ISBN: 9780123965431. Hardcover ISBN: 9780123964885. Imprint. Academic Press. publish date: 30th July 2013 https://www.elsevier.com/books/biomass-gasification- pyrolysis-and-torrefaction/basu/978-0-12-396488-5 [38] Siengchum T, Isenberg M, Chuang SSC. Fast pyrolysis of coconut biomass-an FTIR study. Fuel. 2013;105:559–565. [39] Yang, H., Yan, R., Chen, H., Lee, D. H., and Zheng, C. (2007). "Characteristics of hemicellulose, cellulose and lignin pyrolysis," Fuel 86(12), 1781-1788. DOI: 10.1016/j.fuel.2006.12.013) [40] Nakamura, K., Hatakeyama, T., and Hatakeyama, H. (1981). "Studies on bound water of cellulose by differential scanning calorimetry," Textile Research Journal 51(9), 607-613. DOI: 10.1177/004051758105100909) [41] Zakikhani, P., Zahari, R., Sultan, M. T. H., and Majid, D. L. (2016). “Thermal degradation of four species,” BioResource 11, 414-25. DOI: 10.15376/biores.11.1.414-425 http://www.iaeme.com/IJMET/index.asp 1087 editor@iaeme.com