Mech080830.qxd The Journal of Engineering Research Vol. 6, No. 2 (2009) 33-39 1. Introduction The scarcity of fossil fuels, increasing their costs and increasing the environmental pollution from fossil fuel combustion will make renewable energy sources as more attractive one. Agricultural residue is one form of bio- mass, which is readily available but is largely not utilized in energy recovery schemes. Pyrolysis is one of thermo chemical process which converts the solid biomass in to liquid (bio-oil), gas and solid. The liquid product, pyrolyt- ic oil, approximates to biomass in elemental composition, and is composed of a very complex mixture of oxygenat- ed hydrocarbons. It is useful as a fuel, may be added to petroleum refinery feed stocks or upgraded by catalysts to __________________________________________________ *Corresponding author’s e-mail: ganapathy_sundar@yahoo.com produce premium grade refined fuels, or may have a potential to be used as a chemical feed stocks. Bio-oils are generally preferred products because of their high calorific value, the gross calorific value of the bio oil obtained from pyrolysis of rapeseed oil cake (Suat Ucar and Ahmet, 2008), empty fruit bunches (Abdullah and Gerhauser, 2008) and Cashew nut shell (Das et al. 2004) were 33, 36 and 40 MJ/kg respectively, their ease of trans- portation and storage, their low nitrogen and sulphur con- tent and their opportunity to be converted into chemicals. Coconut shell as an agricultural residue is available abun- dant in India with an annual production of more than 0.94 million tons in the year of 1994 and projected with the production of more than 1.50 million tones for the year of 2010. Coconut shell is more suitable for pyrolysis process, since they contain less amount of ash, more amount of Pyrolysis of Coconut Shell: An Experimental Investigation E. Ganapathy Sundaram*a and E. Natarajanb *aDepartment of Mechanical Engineering, Velammal Engineering College, Chennai 600 066, Tamilnadu, India bInstitute for Energy Studies, College of Engineering, Anna University, Guindy, Chennai 600 025, Tamilnadu, India Received 30 August 2008; accepted 20 January 2009 Abstract: Fixed-bed slow pyrolysis experiments of coconut shell have been conducted to determine the effect of pyrolysis temperature, heating rate and particle size on the pyrolysis product yields. The effect of vapour res- idence time on the pyrolysis yield was also investigated by varying the reactor length. Pyrolysis experiments were performed at pyrolysis temperature between 400 and 600°C with a constant heating rate of 60°C/min and particle sizes of 1.18-1.80 mm. The optimum process conditions for maximizing the liquid yield from the coconut shell pyrolysis in a fixed bed reactor were also identified. The highest liquid yield was obtained at a pyrolysis temperature of 550 °C, particle size of 1.18-1.80 mm, with a heating rate of 60 °C/min in a 200 mm length reactor. The yield of obtained char, liquid and gas was 22-31 wt%, 38-44 wt% and 30-33 wt% respec- tively at different pyrolysis conditions. The results indicate that the effects of pyrolysis temperature and parti- cle size on the pyrolysis yield are more significant than that of heating rate and residence time. The various char- acteristics of pyrolysis oil obtained under the optimum conditions for maximum liquid yield were identified on the basis of standard test methods. Keywords: Slow pyrolysis; Coconut shell; Recycling; Biomass »ÑjôŒ åëH :~æ¡dG RƒL Iô°û≤d …QGô◊G ∫ÓëfE’G ¿ÉLGÎf .EG h ΩQ~æ°S »KÉHÉfÉZ .EG áá°°UUÓÓÿÿGG≈∏Y äɪ«°ù÷G ºéMh ,IQGô◊G ∫~©eh ,∫Óëf’G IQGôM áLQO ÒKCÉJ ~j~– πLCG øe ¢UÉN πYÉØe I~Mh ‘ ~æ¡dG RƒL Iô°û≤d Å£ÑdG ∫Óëf’G ≈∏Y ÜQÉéàdG AGôLCG ” : IQGô◊G áLQO ‘ …QGô◊G ∫Óëf’G ÜQÉŒ AGôLG ” ~bh .πYÉØŸG ∫ƒW Ò«¨J ≥jôW øY ∂dPh ∫Óëf’G Gòg œÉf ≈∏Y QÉîÑ∏d áeÉbE’G âbh ÒKÉJ á°SGQO ” ∂dòch . áŒÉædG á∏¨dG ±hô¶dG ~j~– ” ~bh .º∏e 1^8 - 1^18 Oh~M ‘ äɪ«°ù÷G ΩÉéMCG ™eh ,á≤«bO πµd ájƒÄe áLQO 60 …hÉ°ùj âHÉK Úî°ùJ ∫~©Ãh ,ájƒÄe áLQO 600 ¤G 400 ÚH Ée ¬«∏Y ∫ƒ°ü◊G ” ~æ¡dG RƒL øe ~FÉY πFÉ°S ≈°übG ¿G ~Lh ~bh .~æ¡dG RƒL Iô°û≤d …QGô◊G ∫Óëf’G AÉæKCG ~æ¡dG RƒL øe ~FÉ©dG πFÉ°ùdG øe Q~b ≈°übG ≥«≤– πLG øe ¬«dÉãŸG ¿EG .º∏e 200 πYÉØŸG ∫ƒW h ,á≤«bO πµd ájƒÄe áLQO 60 Úî°ùàdG ∫~©eh .º∏e 1^8 - 1^18 Oh~M ‘ äɪ«°ù÷G ºéMh ,ájƒÄe áLQO 550∫Óëf’G áLQO âfÉc Ée~æY ¤G èFÉàædG Ò°ûJh .áØ∏àıG …QGô◊G ∫Óëf’G ±hôX â– ‹GƒàdG ≈∏Y %30 - 33 h %38 - 44 ,%22 - 31 ÉjhÉ°ùe ¿Éc RɨdG h ,πFÉ°ùdG h ,∫Óëf’G øe π°üëàŸG ~FÉ©dG âjõ∏d ¢üFÉ°üÿG ∞∏àfl ¿G ɪc .áeÉb’G âbhh Úî°ùàdG ∫~©e øe ÒãµH ᫪gG ÌcG »g ∫ÓëfC’G á«∏ªY ~FÉY ≈∏Y äɪ«°ù÷G ºéMh …QGô◊G ∫Óëf’G IQGôM áLQO QÉKBG ¿G .QÉÑàN’G ¥ôW QÉ«©e ¢SÉ°SG ≈∏Y Ég~j~– ~b ” πFÉ°ùdG øe Q~b ≈°übCG ≥«≤ëàd ±hô¶dG π° aG πX ‘ ∫Óëf’G øY áŒÉædG áá««MMÉÉààØØŸŸGG ääGGOOôôØØŸŸGG .ájƒ«◊G á∏àµdG ,ôjh~àdG IOÉYG ,~æ¡dG RƒL Iô°ûb ,Å£ÑdG …QGô◊G ∫Óëf’G : 34 The Journal of Engineering Research Vol. 6, No. 2 (2009) 33-39 volatile matter and available with lower cost in rural areas during all the sessions of the year. Its higher fixed carbon content leads to the usage of solid obtained from the pyrolysis process as an activated carbon material for water treatment purpose. Therefore, a practical method should be applied to pyrolyse coconut shell for providing the valuable product. Ozlem Onay et al. (2006) pyrolyzed rapeseed in a free fall reactor under nitrogen flow to determine the role of pyrolysis temperature and sweeping gas flow rate on the bio-oil yield at atmospheric pressure. Esin Apaydin-Varol et al. [(2007) investigated the effects of temperature on the product yields and its composition of pistachio shell in a slow pyrolysis with fixed bed reactor. Ozlem Onay (2007) performed fast pyrolysis of safflower seed to iden- tify optimum process conditions for maximizing the bio- oil yield in a fixed bed reactor, the optimum process con- ditions were: final pyrolysis temperature 600°C, sweeping gas flow rate 100 cm3/min and heating rate 300 °C/min. Fixed-bed slow and fast pyrolysis experiments have been conducted on a sample of rapeseed to investigate the effects of heating rate, pyrolysis temperature, particle size and sweep gas velocity on the pyrolysis product yields and its chemical compositions by Ozlem Onay et al. (2004). Sevgi Sensoz et al (2008) pyrolyzed safflower seed press cake in a fixed-bed reactor to determine the effects of pyrolysis temperature, heating rate and sweep gas flow rates on the yields of the products using pyrolysis temper- atures between 400 and 600 °C with a heating rates of 10, 30 and 50 °C/min. Ayse E. Putun et al (2002) conducted the slow pyrolysis of soybean cake in a fixed-bed reactor under three different atmospheres: static, for determining the effects of pyrolysis temperature and particle size, nitrogen and steam for determining the product yields. Pyrolysis of corn stalks with batch wise in a laboratory captive sample reactor wire mesh at atmospheric pressure was carried out by Zabaniotou et al (2007) by varying the temperature (470-710 °C) with an average heating rate of 60 °C/s and a reaction time of 0.2 s. The effect of the process conditions such as heating rate, temperature and particle size on the product distribution, gas composition and char reactivity of olive waste and straw at high tem- perature (800 -1000°C) in a free-fall reactor at pilot scale was carried over by Rolando Zanzi et al (2002). Olive bagasse was pyrolyzed in a fixed bed reactor (Sensoz et al. 2006). Alberto J. Tsamba et al (2006) studied the pyroly- sis characteristics and global kinetics of coconut and cashew nut shells. For the coconut shell, the grater mass loss was reported at the temperature interval of 280-415 °C at the heating rate of 10°C/min. The literature study shows, the yield and composition of pyrolysis products greatly depends on the reaction parameters: temperature, particle size of the fuel, heating rate and residence time. Presently, there are limited researches that reported specifically about the effect of temperature, heating rate, particle size and residence time on the product yields of coconut shell pyrolysis. The opti- mum process conditions to produce highest liquid yield from coconut shell are also not available in the literature. Yun Ju Hwang et al (2008) extracted high capacity disor- dered carbons from coconut shells as anode materials for lithium batteries. Afrane et al. (2008) and Gratuito et al. (2008) produced activated carbons from the coconut shells under the physical methods. Dinesh Mohan et al (2008) studied the wastewater treatment by the low cost activated carbons derived from coconut shells and coconut shell fibers. Amudaa et al. (2007) produced a highly effective adsorbent material from the coconut shell combined with aquatic waste for the removal of heavy metal from industrial wastewater. Wei Su et al (2006) pre- pared micro porous activated carbon from raw coconut shell. Furthermore, the former pyrolysis systems, the pyrolysis process were carried out under the flow of inert gas medium and the residence time was varied by means of inert gas flow rate. Hence, some experiments of pyrol- ysis of coconut shell with the effect of different process parameters on the yield of liquid, gas and solid yield are described in this paper. The experiments were conducted with the aim of determining the optimum process condi- tions to maximize the liquid yield from the slow pyrolysis of coconut shell in a fixed bed reactor. 2. Materials and Methods 2.1. Raw Material-Coconut Shell Samples of coconut shell in the present study were originated from Pollachi, Coimbatore district, located in the Tamilnadu, India. Immediately after getting, the coconut shells were sun dried for few days to remove the moisture content, after which they were ground in a high speed rotary cutting mill and screened by standard sieve (IS designation 460-1962) separator to give fractions of less than 0.15 mm, 0.15-0.30 mm, 0.30-0.60 mm, 0.60- 1.18 mm and 1.18-1.80 mm. The fixed carbon, volatiles and ash present in the sample were determined by ASTM standards. The elements carbon, hydrogen, nitrogen, oxy- gen and sulphur content on the sample were also identified by the ASTM standards. The calorific value and moisture content of the sample were measured with ASTM D 5865:2007 and ASTM D 3173:2003 standards respective- ly. The properties of sample, components and elements are given in Table 1. Components Volatiles 72.93% Fixed carbon 19.48% Ash 0.61% Elemental analysis a (%) Carbon 53.73% Hydrogen 6.15% Oxygen b 38.45% Nitrogen 0.86% Sulphur 0.02% Calorific value (MJ /kg) 20.88 Moisture content (%) 6.98% Table 1. Components and elemental analysis of Coconut shell a Weight percentage on dry basis b By difference 35 The Journal of Engineering Research Vol. 6, No. 2 (2009) 33-39 2.2. Experimental Apparatus and Procedure As shown in Fig. 1, the 316 stainless steel tubular reac- tors with a length of 200 mm and 300 mm, and an inter- nal and external diameter of 27 mm and 33 mm were used to conduct the experiments, respectively. In each run, a 15 g of the sample biomass was placed inside the reactor then the reactor was placed inside the electric furnace with the capacity of 2 kWh, which was specifically designed and manufactured for this study. The reactor was heated exter- nally by an electric furnace. The temperature inside the reactor was measured by a Cr - Al: K type thermocouple. The temperature and heating rate was controlled by an external PID (Proportional-Integral-Derivative) con- troller. A 6.5 mm ID and 9 mm OD stainless steel pipe was used to connect the reactor and glass condenser. The con- necting pipe between the reactor and the condenser sys- tem was maintained at 200°C to avoid condensation. The condensable liquid products (bio-oil + water) were col- lected in a 300 mm length coil type glass condenser. The temperature of the condenser was maintained at 25°C by circulating the water in the condenser. After each experi- ment, the condensed liquid was collected into the sample bottle and the liquid weight was calculated by the weight difference of sample bottle before and after the liquid was collected. After pyrolysis, the solid residue was removed and weighed. Then the gaseous phase was calculated from the material balance. The biomass sample input, liquid and solid char were measured by the electro balance weighing machine with an accuracy of +/ - 0.01 g. All the yields were at an average yield of at least three with an experimental measurement error of less than ± 1.5%. The experiments performed in the fixed-bed reactor were carried out in four groups. In the first, to determine the effect of the pyrolysis temperature on the coconut shell pyrolysis yields, a 15 g of the sample with the particle size of 1.18-1.80 mm was placed in the 200 mm length reactor then the reactor was placed inside the furnace and the tem- perature was raised at 60 °C/min to a final temperature of either 400, 450, 500, 550, or 600 °C and held for until no further significant release of gas was observed. The sec- ond group of experiments was performed in order to deter- mine the effect of particle size on the pyrolysis yields. The experiments were conducted at particle sizes less than 0.15 mm, 0.15-0.30 mm, 0.30-0.60 mm, 0.60-1.18 mm or 1.18-1.80 mm. For all these experiments, the heating rate, the final pyrolysis temperature (based on the results of first group of experiments) and the reactor lengths were 60°C /min, 550 °C and 200 mm respectively. The third group of experiments was performed in a 200 mm length reactor to determine the effect of heating rate on the pyrolysis yield. At first, 15 g of sample was placed in the reactor then the reactor was placed inside the fur- nace and the temperature was raised at either 20 °C/min, 40°C/min or 60 °C/min by PID controller. For all these experiments, the final pyrolysis temperature and particle size were 550 °C and 1.18-1.80 mm respectively, based on the results of the first and second group of experiments. Finally, the effect of residence time on the pyrolysis yield was determined by varying the reactor lengths. The exper- iments was performed with the reactor lengths of 200 mm and 300 mm. Based on the first three groups of experi- ments the final pyrolysis temperature, particle size and heating rate were maintained at 550 °C, 1.18-1.80 mm and 60 °C/min respectively. The pyrolysis oil obtained at optimum condition was tested for its properties and functional groups. Fourier transform infrared spectroscopy (FT-IR) analysis was per- formed on a Perkin Elmer Spectrum device with a Resolution of 1.0 cm-1 for finding the functional groups present in the bio oil. 3. Results and Discussion 3.1 Effect of Temperature on the Pyrolysis Yield Figure 2 presents the product distribution from slow pyrolysis of coconut shell at a pyrolysis temperature of 400 - 600 °C. The liquid and gas yield were increased from 38 to 43 wt% and 30 to 33 wt% respectively, when the pyrolysis temperature was increased from 400 to Thermocouple Reactor Furnace Condenser Thermocouple Oil Figure 1. Pyrolyser Experimental Setup 36 The Journal of Engineering Research Vol. 6, No. 2 (2009) 33-39 600°C, whereas the solid yield significantly decreased from 32 to 22 wt%. The decrease of liquid yield and increase of gas yield were observed at higher temperature. The decrease in liquid and gas yield at lower temperature is due to incomplete decomposition of the shell (pyrolysis is not complete). Decrease in liquid and char yield and increase in gas yield at higher temperature is due to not only the secondary cracking of pyrolysis vapor but also solid char. Similar results were observed in the fixed - bed slow pyrolysis of rapeseed at 30°C/min in which the liq- uid yield increased from 41 to 47 wt% when the pyrolysis temperature increased from 400°C to 550 °C (Ozlem and Kocker, 2004), but the liquid yield of safflower seed press cake and soybean cake were found to be 30 to 33 wt% and 26 to 30 wt% respectively at the same temperature range (Sensoz and Angin, 2008; Putin et al. 2002). This similar- ity and variation of the liquid yield could be due to the variation of the components present with individual bio- mass. 3.2. Effect of Particle size on Pyrolysis Yield From Fig. 3, the solid and liquid yields are significant- ly increased as the particle size is increased from less than 0.15 mm to1.80 mm and gas yield is found to decrease. The study found that solid and liquid yield increases from 23 to 26 wt% and 37 to 43 wt% respectively and gas yield decreases from 39 to 30 wt% when the particle size is increased from less than 0.15 to 1.18-1.80 mm. The increases in the solid yield with the increasing particle size for the sample biomass could be due to greater tempera- ture gradient inside the particles. So that at a given time the core temperature is lower than that of the surface, which possibly gives rise to an increase in the solid yield (Zanzi et al. 2002). Decrease in particle size leads to decreases of liquid yield because the residence time of the volatiles in the reactor is longer, favor the cracking of hydrocarbons, when smaller particles are used (Sensoz et al. 2000). More residence time of volatiles inside the reactor leads to cracking of heavier molecules (tar) in to lower molecules at lower particle size ranges and it results in increase of gaseous product. There is a significant effect of particle size on the char, oil and gas yield in the pyrol- ysis of olive bagasse and pine sawdust (Sensoz et al. 2006; Wei et al. 2006). 3.3. Effect of Heating Rate on Pyrolysis Yields Figure 4 shows the pyrolysis product yields of coconut shell at different heating rates of 20, 40 and 60 °C/min with a constant pyrolysis temperature of 550 °C and par- ticle size of 1.18-1.80 mm in a 200 mm length reactor. The liquid yield was low at lower heating rate and increased with increase of heating rate; the liquid yield was 40 wt% at the heating rate of 20 °C/min and increased to 43 wt% when the heating rate increased to 60°C/min. The gas yield also increased with increase of heating rate, but the char yield decreased with the increase of heating rate. The char yield was decreased from 29% to 25 wt% when the heating rate increased from 20 °C/min to 60 °C/min (Fig. 4). The increase of the oil yield with the increase of heat- ing rate may be due to higher heating rates that break the heat and mass transfer barriers in the particles (Haykiri et al. 2006). The cracking of the pyrolysis vapors at higher heating rates leads to increase of gas yield. The same trend was predicted by other researchers (Sensoz 2003; Sensoz and Angin, 2007; Onay 2007 and Karaosmanoglu et al. 1999) on pine bark, Safflower seed press cake, pistacia khinjuk seed and straw and stalk of the rapeseed plant. 3.4. Effect of Residence Time on Pyrolysis Yield The effect of residence time on the pyrolysis yield was investigated by varying the reactor length. Figure 5 shows the influence of residence time on the pyrolysis yield. The gas yield from 300 mm reactor was higher than that from the 200 mm length reactor. The liquid yield from 200 mm reactor was higher than that from the 300 mm reactor. This Figure 2. Yield of pyrolysis products at various pyrolysis temperatures 15 20 25 30 35 40 45 <.15 .15-.30 0.30- 0.60 0.60- 1.18 1.18- 1.80 Particle Size (mm) P yr ol ys is Y ie ld (% ) Solid Liquid Gas Figure 3. Yield of pyrolysis products with different particle size 20 25 30 35 40 45 20 40 60 Heating Rate (°C/min) P yr ol ys is Y ie ld (% ) Solid Liquid GAs Figure 4. Effect of heating rate on pyrolysis yield 37 The Journal of Engineering Research Vol. 6, No. 2 (2009) 33-39 shows the opposite trends in the liquid yield. This could be due to the secondary cracking of the liquid yield in the 300 mm length reactor due to prolonged residence time of the vapours inside the reactor. The solid residue yield in 300 mm reactor was higher than that in the 200 mm reac- tor. 4. Properties of Pyrolysis Oil Physical properties were determined for the bio-oil using the American Standards for Testing and Materials (ASTM). The physical, chemical properties and calorific value of the bio-oil obtained under optimum conditions are given in Table 2. The IR spectrum of the bio-oil at optimum condition is given in Fig. 6. The O-H stretching vibrations between 3200 and 3400 cm-1 indicate the presence of phenols and alcohols. The C-H stretching vibrations between 3200 and 3400 cm-1 and C-H deformation vibrations between 1350 and 1475 cm-1 indicate the presence of alkanes. The C=O stretching vibrations with absorbance between 1650 and 1750 cm-1 indicate the presence of ketones or aldehy- des. The absorbance peaks between 1575 and 1675 cm-1 represent C=C stretching vibrations indicative of alkenes and aromatics. The C-H stretching and bending vibrations between 1380 and 1465 cm-1 indicates the presence of alkane groups in pyrolysis oils derived from biomass. Absorptions between 1300 and 900 cm-1 indicates the carbonyl components (ie. alcohols, esters, carboxylic acids or ethers). The absorbance peaks between 900 and 690 cm-1 represent O-H stretching vibrations indicative of aromatic groups. Properties Bio-oil Elemental (wt %) Carbon 75.4 Hydrogen 11.7 Nitrogen 2.4 Oxygen 10.5 Density (kg/m 3) 1090 Viscosity, 50°C (cSt) 36 Flash Point (°C) 80 Higher heating value (MJ/kg) 38.6 Table 2. Properties of bio-oil under optimum conditions 3 5 0 0 3 0 0 0 2 5 0 0 2 0 0 0 1 5 0 0 1 0 0 0 5 0 0 0 2 0 4 0 6 0 8 0 1 0 0 1 3 6 8 1 0 2 4 7 5 7 1 1 1 5 1 464 12661 713 285 5T ra n sm itt a n ce % w a ven um b er (cm -1 ) 3418 2933 1 515 Figure 6. FT - IR spectra of pyrolysis oil Comparison of liquid yield in 200 mm and 300 mm sectors L iq ui d Y ie ld ( % ) Particle Size (mm) Particle Size (mm) So lid Y ie ld ( % ) Particle Size (mm) G as Y ie ld ( % ) Figure 5. Effect of residence time on pyrolysis yield 38 The Journal of Engineering Research Vol. 6, No. 2 (2009) 33-39 5. Conclusions In this study, pyrolysis experiments of the coconut shell are carried out in a fixed bed reactor with different pyrol- ysis temperature, particle size, heating rates and reactor length. The bio oil obtained at the optimum parameters are tested for finding its properties. The following are the findings from pyrolysis experiments of coconut shell in the fixed bed reactor: . The optimum process conditions for maximizing the liquid yield of slow pyrolysis of coconut shell in a fixed bed are: pyrolysis temperature 550 °C, particle size 1.18-1.80 mm, heating rate 60 °C/min and the reactor length 200 mm. The maximum liquid yield of 45 wt% was obtained at the optimum condition. . Employing higher particle size results in more amounts of liquid and solid yield and less amount of gas yield compared to lower particle size. The gas yield decreases from 40 to 30 wt % when particle size is increased from less than 0.15 to 1.8 mm. . The liquid yield increased from 40 to 43 wt% when the heating rate was increased from 20 °C/min to 60°C/min. The effect of heating rate on the pyrolysis yield is not significant compared to other parameters in this study. . The rapid devolatilization of cellulose and hemi cellu- lose increased the pyrolysis conversion from 69 to 88 wt% when the temperature was increased from 400 to 550°C. . The maximum liquid yield of 43 wt% and 35 wt% were obtained at reactor length of 200 mm and 300 mm respectively. . The elemental composition of bio-oil is found to be bet- ter than that of feedstock. The heating value of the bio-oil is found to be similar to that of diesel fuel. FTIR analysis showed that the bio-oil composition was dominated by oxygenated species. 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