Adiabatic Fixed-Bed Gasification of Colombian Coffee Husk Using Air-Steam Blends for Partial Oxidation
Adiabatic Fixed-Bed Gasification of Colombian Coffee Husk Using Air-Steam Blends for Partial Oxidation
Javier Bonilla1 and Gerardo Gordillo2
1Mechanical Engineering Department, Universidad ECCI, Cra 19 No. 49-20, Bogotá, Colombia
2Mechanical Engineering Department, Universidad de los Andes, Cra 1 Este No. 19A-40, Office ML 652, Bogotá, Colombia
Correspondence should be addressed to Javier Bonilla; oc.ude.icce@pallinobj
Received 9 February 2017; Revised 21 June 2017; Accepted 19 July 2017; Published 13 September 2017
Academic Editor: Constantine D. Rakopoulos
Copyright © 2017 Javier Bonilla and Gerardo Gordillo. This is an open access article distributed under the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original work is properly cited.
The increasing energy consumption, mostly supplied by fossil fuels, has motivated the research and development of alternative fuel technologies to decrease the humanity’s dependence on fossil fuels, which leads to pollution of natural sources. Small-scale biomass gasification, using air-steam blends for partial oxidation, is a good alternative since biomass is a neutral carbon feedstock for sustainable energy generation. This research presents results obtained from an experimental study on coffee husk (CH) gasification, using air-steam blends for partial oxidation in a 10 kW fixed-bed gasifier. Parametric studies on equivalence ratio (ER) (1.53 < ER < 6.11) and steam-fuel (SF) ratio (0.23 < SF < 0.89) were carried out. The results show that increasing both SF and ER results in a syngas rich in CH4 and H2 but poor in CO. Also, decreased SF and ER decrease the peak temperature at the gasifier combustion zone. The syngas high heating value (HHV) ranged from 3112 kJ/SATPm3 to 5085 kJ/SATPm3 and its maximum value was obtained at SF = 0.87 and ER = 4.09. The dry basis molar concentrations of the species, produced under those operating conditions (1.53 < ER < 6.11 and 0.23 < SF < 0.89), were between 1.12 and 4.1% for CH4, between 7.77 and 13.49% for CO, and between 7.54 and 19.07% for H2. Other species were in trace amount.
The actual growth in energy consumption, supplied mostly by fossil fuels that produce greenhouse and pollutant gases (, ) through combustion processes, requires effective solutions to decrease the humanity’s dependence on this type of fuels. Biomass feedstock (neutral carbon fuel), which includes energy crops and municipal, animal, and crops wastes, is a good renewable source for energy conversion via thermal processes such as full combustion and gasification. Combustion and gasification of biomass are processes that do not increase the carbon in the atmosphere since the carbon content in biomass has been previously taken from the ambient through the photosynthesis process. Due to the fact that biomass is considered a low heating value fuel, it is more appropriate for gasification than for direct combustion since combustion biomass can lead to combustion instability. Full combustion and air-biomass gasification have been deeply studied for a long time [1, 2]. However, air-steam, oxygen-steam gasification, pyrolysis, and steam reforming gasification are new technologies recently studied, in order to improve the quality of syngas and liquid fuel produced. Colombia is the third coffee-producer around the world . During 2015, Colombia produced 14.2 millions of green coffee (1 sack = 60 kg.) sacks (the terminus green coffee or gold coffee is the name for coffee bean after it has been separated from its wrappers through the shelling process) . Coffee husk (CH) is a by-product from coffee seed shelling; for example, 100 kg of coffee seed produces about 86 kg of green coffee and 14 kg of CH , which leads to a production of about 138697 tons of CH per year in Colombia. In Colombia, many coffee agroindustries do not have the appropriate CH, waste handling infrastructure, which could result in the pollution of natural sources . Using CH wastes as feedstock for locally placed gasification can reduce both the pollution generated by coffee industries and the dependence of these industries on fossil fuels.
In an updraft fixed-bed gasifier, the biomass undergoes four stages, known as drying, pyrolysis, reduction, and oxidation . Each of these stages occurs in a certain zone, as shown in Figure 1. The biomass enters at the top of the gasifier and goes down to the drying zone (373 K < T < 450 K) where the moisture content is released . Afterwards, the biomass descends to the pyrolysis zone (450 K < T < 900 K) to release the Volatile Matter (VM) and to produce char, which descends to the reduction zone where the C atoms reacts with gases (H2O, CO2, and H2) coming from the combustion zone to produce secondary products such as CO, H2, and CH4 . The remaining char, from the reduction zone, passes to the combustion zone where the C atoms are oxidized with the oxygen from the air supplied to produce CO and CO2 and the heat required to drive the system. Also, in the combustion zone the C atoms from biomass react with the H2O supplied to produce CO and H2. Due to the fact that in a fixed-bed gasifier the different stages of biomass gasification occur in different zones, those gasifiers are the most appropriate to control some reactions and to produce certain desired species as required . The oxidizer in gasification processes may be air , pure oxygen, pure steam , or blends of these [13–16].
Figure 1: Stages and reactions in a fixed-bed gasifier, adopted from .
During biomass gasification, many parallel and competitive chemical reactions take place, making it a chemically complex process . However, the global biomass gasification process can be reduced to a set of global reactions as shown in Table 1. Reaction enthalpies lower than zero and higher than zero imply exothermic and endothermic reactions, respectively. Reactions (), (), and () are heterogeneous reactions occurring in the oxidation zone, whereas reactions () and () are typically heterogeneous reactions that occur in the reduction zone. Homogeneous reactions usually happen in the upper reactor zones. The species leaving the reactor depend on operating parameters such as temperature, pressure, species concentration, biomass particle size, and residence time . The time for developing heterogeneous reactions is much longer than those for homogeneous reactions.
Table 1: Chemical reactions in gasification process, adapted from [9, 21, 22].
Air-blown gasification processes of wood and coal have been used during a long time to produce a syngas basically composed of CH4, CO2, CO, N2, H2, and H2O. Due to the necessity of improving syngas quality (gases rich in H2), other gasification processes, which use air-steam, oxygen-steam, and pure steam as oxidizing source in different gasifiers (fluidized-bed, cross draft, etc.), have been studied [23, 24]. Mostly, gasification using air or pure oxygen as oxidizing source produces a syngas with high CO and CH4 concentrations, whereas gasification with steam or mixtures of air or oxygen with steam results in a syngas rich in H2 [22, 25]. Typically, gasification using only steam (steam reforming) is an endothermic process that produces a mixture of H2, CO, and CO2 .
In 2008, Gao et al.  performed a study on the hydrogen production using pine sawdust in a counter-current fixed-bed gasifier. The parameters investigated were temperature, the steam-biomass (S/B) ratio, and equivalence ratio (ER (In  .)). In this research, the tar generated in the gasification process was cracked using a porous ceramic reformer. Thus, hydrogen concentration was higher than that without using a porous ceramic reforming. In 2009, Gordillo and Annamalai  performed a study on dairy biomass adiabatic gasification carried out in a fixed-bed gasifier and using air-steam blends as oxidizing source. The effects of ER and SF on syngas composition (H2, CO, CO2, N2, CH4, and C2H6), temperature profiles, syngas HHV, and energy conversion were discussed. In 2008, Plis and Wilk  discussed the gas yield in a 50 kW/hr fixed-bed gasifier using air as oxidizer and wood pellets as fuel biomass. Parametric studies on the experimental performance, , and the biomass MC (moisture content) were developed. The syngas produced in this study was blended with coal to run a cocombustor. In 2009, Vélez et al.  carried out an experimental study on fluidized-bed cogasification of coal with biomass using a mixture of air-steam as oxidizing source. Blends of coal with 6%–15% of coffee husk (CH), rice husk (RH), and sawdust contents were used as feedstock. The parameters studied were Rac and Rvc ranging from 2 kg/kg to 3 kg/kg and from 0.1 kg/kg to 0.8 kg/kg, respectively. The effects of these parameters on syngas HHV were discussed. In 2010, Wilson et al.  gasified coffee husk using oxygen-nitrogen/steam blends at different gasification temperatures (900°C, 800°C, and 700°C), concluding that increasing temperature resulted in a linear increase in the CO content in syngas. At lower O2 concentrations, the above effect is more pronounced. When gasification temperature was increased from 700°C to 900°C, the CO produced, at 2% of O2, was enhanced by 6 and 2.5 times in a pure N2 environment. In 2011, Gordillo and Rodriguez  published a modeling study on coffee gasification using air-steam as oxidizing source. The Chemical Equilibrium with Applications program (CEA), developed by NASA, was used to estimate the effect of equivalence ratio (ER) and steam to fuel (SF) ratio on equilibrium temperature and gas composition of ~150 species. The results showed that increased ER and (S : F) ratios produce mixtures that are rich in H2 and CO2 but poor in CO.
From the literature review, it is apparent that there are no preliminary experimental studies on Colombian coffee husk gasification using air-steam blends in a fixed-bed counter-current gasifier. The current paper presents results obtained from an experimental air-steam fixed gasification study of coffee husk. The effects of operating parameters, such as equivalence ratio (ER) and steam to fuel (SF) ratio, on temperature profile along gasifier axis, syngas composition, syngas HHV, and energy recovery, are discussed. Typically, results obtained from this research were = 5085 kJ/m3 and molar concentration (dry basis) H2 = 19.07%; CO = 13.49%; CO2 = 21.78%; and CH4 = 4.1%. These results are discussed and analyzed in the current paper.
Full or stoichiometric combustion occurs when it is used only the necessary amount of O2 for total oxidation of the atoms contained in the fuel (see (1)). This process (stoichiometric combustion) is basically used to produce heat.
On the other hand, partial oxidation or gasification (rich mixtures) uses lower oxygen than that required for theoretical combustion and produces a fuel gas known as syngas. According to the desired syngas composition, the gasification process must be carried out using different oxidizing sources such as pure air, pure oxygen, or pure steam. Also, mixtures of air or oxygen with steam are used. Equation (2) shows an air-steam biomass reaction producing only the most important species. The composition of syngas produced, under air-steam biomass gasification, typically, depends on some operating parameters such as equivalence ratio (ER, see (3)) and steam to fuel (SF, see (4)) ratio.
2. Material and Methods2.1. Experimental Facility
Figure 2 shows a diagram of the experimental facility used in the study. The facility consists of (i) a biomass hopper where biomass is stored; (ii) a 102 cm tall small-scale (10 kW/hr.) updraft fixed-bed gasifier, built of castable alumina refractory tube (inner and outer diameter of 127 mm (5 in) and 25.4 cm (10 in), resp.), surrounded by 5.08 cm fiberglass insulating blanket layer in order to reduce heat lost; (iii) a steam generator built of a 10 cm internal diameter stainless steel tube, surrounded by a heating tape element, with variable power output (350–1000 W) to control vapor flow rate generation from 1.27 g/min to 17.25 g/min; (iv) an ash collector system consisting of a conical vibrating grate and an ash deposit placed under the grate. The conical grate (drilled with several holes) was built of cast iron and attached to a pneumatic vibrator to maintain continuous ash removal and hence quasi-steady-state operating conditions; (v) a cleaning and drying system, composed of filters and condensers to clean and dry, respectively, the syngas samples; condenser was cooled using cold water at 0°C; (vi) a temperature recorder system to record every minute the temperature measured by eight K-type thermocouples placed at 8 different points through the bed; (vii) a gas analyzer system where the syngas, previously cleaned, is analyzed; this gas analyzer analyzes and records mole fraction of CO, CH4, H2, CO, CO2, and ; and (viii) a combustion chamber to burn the syngas leaving both the gasifier and the gas analyzer.
Figure 2: Schematic gasification facility, adapted from .
2.2. Operating Conditions and Procedure
The experimental procedure was performed according to the parameters shown in Table 2.
Table 2: Experimental parameters.
Every experiment started with preheating the gasifier using a propane torch just located under the grate. When the temperature, 2 cm above the grate, was about 550°C (about 25 minutes after having turned on the torch), the torch was turned off and the screw feeder started to supply biomass to the gasifier until the bed height was about 18 cm. Then, the air and steam started to be supplied to the gasifier at flow rates as required to maintain the desired experimental operating parameters (ER and SF) shown in Table 2. At this time, the temperature started to be measured and stored using the temperature data logger. As biomass was gasified the bed height decreased and ash accumulated on the grate. Then, biomass was added every 10 minutes and in batches as required. Also, ash was continuously removed from the top of the grate to the gasifier plenum through the vibrating grate, whose vibrating frequency was adjusted to maintain a constant 2 cm- thickness ash layer. When the gasification system stabilized, that is, peak temperature, measuring 2 cm above of the grate, started to be constant, without changing its position, the gas samples, taken from the top of the gasifier at a rate of 1 L/min, were cleaned and dried to analyze their composition (CO2, CO, CH4, C2H6, H2, O2, and N2), at real time and during 10 minutes, by the gas analyzer whose ranges are CO2 between 0 and 40%, CO between 0 and 30%, CH4 between 0 and 10%, H2 between 0 and 40%, and C2H6 between 0 and 5%. For all experiments, the biomass flow rate was maintained constant at 600 g/h while the flows rates of air and steam were adjusted at the values given in Table 2 in order to maintain the desired operating (ER and SF) conditions. For all experiments, the air and steam were supplied to the gasifier at 75 kPa and temperatures of 20°C and 92°C, respectively, The temperatures along the gasifier bed were measured by k-type thermocouples placed at 2, 4, 6, 8, 10, 12, 14, and 16 cm above the cast iron grate and recorded, at real time, every minute by the temperature recorder.
3. Results and Discussion3.1. Uncertainty Analysis
The uncertainty at measurements of temperature, air flow, fuel flow, and syngas compound were found by the following equations that calculate the total uncertainty and uncertainty propagation, respectively.where is function of measured variables of , , are uncertainties of and , respectively, and and are systematic uncertainties and random uncertainties of . The temperatures in the gasifier bed were measured by k-type thermocouples with a ±0.75% accuracy in the range of measured temperatures. The uncertainty derived from thermocouple operation was taken to ±0.15%. Then, the total uncertainty of temperature is ±0.76% by (5). The air flow was measured by a rotameter with 100 SFCH full scale (2.83 m3/h) and resolution of 5 SFCH (0.14 m3/h) and accuracy of ±4%; the total uncertainty of air flow is ±4% by (5). A rotameter with 9.96 cm3/min full scale and 0.066 cm3/min resolution was used to measure the water flow to the gasifier. This rotameter has an accuracy of ±1%. Thus, total uncertainty to water flow is ±1%. The feeding system (screw feeder) was calibrated previously and its systematic uncertainty was ±3.42%. The total uncertainty of scale used to measure the sample weight was ±1%, whereas the total uncertainty of the timer used to measure the feed rate was ±3.87%. The uncertainties of ER and SF are functions of two variables, which were calculated by using (6), resulting in ±5.57% for ER and ±4.12% for the SF ratio. The total uncertainty to every syngas compound is function of ±1% accuracy only. Table 3 summarizes total uncertainties.
Table 3: Uncertainty of gasification parameters.
3.2. Fuel Characterization
CH samples were obtained from the Colombian coffee agroindustry and were characterized by ultimate and proximate analyses. Table 4 shows results from these analyses along with the empirical formula that was derived using atom balance on compounds. Also, mesh size particle of samples was determined and results are shown in Table 5.
Table 4: Proximate and ultimate analysis of CH.
Table 5: Mesh particle size characterization of CH.
3.3. Temperature Profiles
Figures 3–8 show results on temperature profile along the gasifier axis for different ER and SF ratios. Although experimentation was carried out at 1.53 < ER < 6.11, temperature profiles are shown only for ER of 1.53, 3.07, 4.09, and 6.11. Temperature data is given at quasi-steady-state conditions. Full steady state conditions were impossible to achieve due to batch biomass supply. The tendency of the curves shows that increasing ER tends to decrease temperatures due to less air supplied to the gasifier. This leads to decreased char oxidation rate, because char oxidation is diffusion controlled; hence its rate depends on the oxygen available in the combustion zone. Lower char oxidation rates result in lower temperatures, since char oxidation (heterogeneous reactions 3 and 4) is an exothermic process that releases the heat required for the global gasification. The temperatures peaks, shown in the curves trend from Figures 3–8, show the place where the char oxidation occurs. For almost all experimentation cases the char oxidation occurred 4 cm above the grate, indicating that quasi-steady-state was achieved. When fixed gasification is carried out under unsteady operating conditions the maximum temperature in the combustion zone move up through the gasifier axis due to ash accumulation on the grate. In the current experimentation the ash was removed to the gasifier plenum by a vibrating grate.
Figure 3: Temperature profile along with gasifier axis at SF = 0.
Figure 4: Temperature profile along with gasifier axis at SF = 0.23.
Figure 5: Temperature profile along with gasifier axis at SF = 0.38.
Figure 6: Temperature profile along with gasifier axis at SF = 0.59.
Figure 7: Temperature profile along with gasifier axis at SF = 0.87.
Figure 8: Temperature peaks versus ER for several SFs.
It is apparent from these results that increased SF ratios also decrease peak temperatures (Figure 8). Increased SF implies more steam supplied to the gasifier; hence the reaction of char in the combustion zone takes place under reach-steam conditions, which implies more of the char reacting with the steam through the endothermic reaction to produce H2 and CO. The maximum peak temperature (960°C) was reached for air-gasification (SF = 0) due to no H2O in the combustion zone.
Also, results from temperature profile show that temperatures at 2 cm above the grate are lower than these at the combustion zone (peak temperature), indicating that at this point (2 cm above the grate) there is ash accumulation. On the other hand, the temperature, above the combustion zone (4 cm up to the grate), decreases since the reactions occurring at these zones (reduction, pyrolysis, and drying) are endothermic.
3.4. Gas Composition
In this section (Figures 9–11), the results on syngas composition are presented for only relevant species in a dry tar free basis. Species in trace amount are not shown. Figure 9 illustrates the H2 content in syngas as a function of ER for several SFs. It is apparent that H2 production increases when both ER and SF are increased. Increasing SF, at constant ER, leads to an H2O-rich combustion environment, so those reactions ( and ), which produce H2, are favored. That is, steam reforming reaction (reaction ), which produces H2 and CO through the reaction of C atoms with H2O, takes place in the combustion and reduction zones (4 cm above the grade) where all water vapor supplied with the air is available. Thus, the char reaction occurs in an H2O-rich mixture. which increases the reaction rate of char, resulting in high productions of H2 and CO. However, Figure 10 shows a decreased production of CO while SF increases, which suggest that much of the CO produced by the steam reforming reaction () in the combustion and reduction zones is consumed by the shift reaction () in the upper zones (pyrolysis and drying) to produce more H2 and CO2.
Figure 9: H2 production versus ER for several SFs.
Figure 10: CO concentration at several SFs versus ER.
Figure 11: CO2 concentration at several SFs versus ER.
In general, results show that H2 increases and CO decreases with increased ER. At constant SF, increasing ER implies less O2 supplied to the gasifier, resulting in H2O-rich mixtures that are favorable for the reaction of char with H2O (reforming reaction) to produce H2 and CO. Also, higher ER leads to lower combustion temperatures (peak temperatures), which are more appropriate for the production of CO2 than CO, via char oxidation (reaction ). Oxidation of char to produce CO and CO2 via reactions and is competitive, and their reaction rates are very dependent on the temperature; low temperatures favor the production of CO2 through reaction . Less production of CO implies more O2 free to react with remaining char and hence more CO2 (Figure 11).
From Figure 9, it is apparent that the variation of ER is more important on the H2 production at lower SF ratios than at higher SF: at SF = 0.23, increasing the ER from 1.53 to 6.11 increases the H2 production by 79%, whereas at SF = 0.87, the same increase (1.53 to 6.11) in the ER only rises the H2 production by 44.3%. On the other hand, at ER = 1.53, increasing SF from 0.23 to 0.87 increases the H2 concentration by 75.2%, but, at ER = 6.11, the same increase in SF (0.23 to 0.87) only increases the H2 production by 41.2%. This suggests that the influence of SF on the H2 production is more important at lower ER than at higher ER.
For all SF, the slopes of CO-curves are higher at ER > 3.51 than those at ER ≤ 3.5 (Figure 10). In other words, for any increase in ER the decrease in CO is higher at ER > 3.51 than at ER < 3.51 (i.e., at SF = 0.87, increasing ER from 1.54 to 3.51 decreases CO by about 8% while increasing ER from 3.51 to 6.11 decreases CO by about 30%). The effect of increased ER on the decrease of temperature peak (combustion zone) is higher at ER > 3.51 than that at ER < 3.51 (Figure 8). Thus, increasing ER decreases more the production of CO, via reaction , at ER > 3.51 than at ER < 3.51. Also, it is apparent that (oxidation of char to produce CO2) is more important at ER > 3.51 than at ER < 3.51.
Figure 12 shows CH4 production as a function of ER for different SF. Increasing both ER and SF increases H2 production (Figure 9). Thus, the production of CH4, via the heterogeneous reaction , is favored (Figure 12) due to higher H2 concentration in the reduction zone. The maximum CH4 was about 4.1%, which indicates that most of the CH4 produced in the reduction zone, via reaction , is consumed by the reforming of CH4 () above of the reduction zone.
Figure 12: CH4 concentration at several SFs versus ER.
3.5. HHV of Syngas and Energy Conversion Efficiency
The syngas higher heating values (HHV), calculated by (7), are presented in Table 6 as a function of ER and SF. where and are the molar fraction and higher heating value of each gas fuel, contained in syngas, respectively. is the high heating value (kJ/SATP m3 of dry syngas).
Table 6: Dry basis syngas HHV [kJ/SATP m3] for several SF and ER ratios.
Table 6 presents results on for different ER and SF. At SF = 0.23 increased ER increases . However, at SF ≥ 0.38, the presents a maximum value at ER = 3.51 or ER = 4.09. In general, increases with a higher ER, because the syngas has more CH4 content ( = 36339 kJ/SATP m3 of CH4). According to the results, the H2 content in syngas is inversely proportional to the CO content; more H2 implies less CO. This suggests that the increases with increased ER, mainly, due to more production of CH4, since the energy density of CO (11567 kJ/SATP m3 of CO) is very similar to that of the H2 (11600 kJ/SATP m3 of H2).
Although gives information on syngas energy density, it does not give information on energy recovered in syngas for each biomass unit gasified. The energy recovery (dry tar free basis) was estimated using the following:where is the higher heating value of syngas on a dry basis, and are the moles of biomass and steam supplied to the gasifier, respectively, by each normal m3 of dry syngas produced, corresponds to the gross heating value of DAF fuel (kJ/m3), and is the vaporization enthalpy of water (kJ/kg_K.). Since it was impossible to measure flows rates of both tar and water in the syngas, the syngas flow rate, required to estimate energy recovery, was estimated using atom balance on reactants (biomass, air, and steam) and products (tar composition, char, water in syngas, and dry syngas composition). Table 7 presents dry tar free energy recovery, which refers to energy recovered in syngas for each unit biomass gasified. The remaining energy is in tar, char, and energy lost by radiation and convection on the outside walls of the reactor.
Table 7: Dry tar free energy recovery for several ER and SFs.
From the results presented in Table 7, it can be concluded that increased ER tends to reduce energy recovery, whereas energy recovery increases with a higher SF. In general, the energy recovery ranged between 14% and 62%; the remaining percentage of energy is in tar, char, and latent heat of syngas.
(i)The temperature in the combustion zone ranged from 521°C to 960°C. Lower values of peak temperature are because of higher SFs, which favor the endothermic char reforming reaction . Above the combustion zone (4 cm up to the grate), temperature decreases because of the presence of endothermic reactions in the reduction, pyrolysis, and drying zones, with the exception of the shift reaction .(ii)Increasing both ER and SF produces mixtures rich in H2, CH4, and CO2, but poor in CO, due to the fact that H2 and CO2 are competitive species with CO, via the shift reaction . Also, CO and CO2, produced by char oxidation via reactions and , are competitive. H2 content in the syngas ranged from 7.54% to 19.07%, whereas CO content in syngas was from 7.77 to 13.49%. On the other hand, the maximum CH4 content was of 4.10%.(iii)HHV of syngas varied from 3112 kJ/SATP m3 to 5085 kJ/SATP m3. Those values are similar to the ones reported in previous gasification studies. That is, high heating values (HHV), ranging from 3268 kJ/SATP m3 to 4581 kJ/SATP m3, were reported by  Gordillo and Annamalai, for a syngas obtained from air-steam dairy biomass gasification.(iv)The quality of syngas produced highly depends on operating parameters such as ER and SF. If rich-H2 syngas mixtures are desired, gasification must be carried out under higher ER and SF ratios.(v)Air-steam gasification of coffee husk is possible without heat addition under 1.54 < ER < 6.11 and 0.23 < SF < 0.87. At ER > 6.11 and SF > 0.87, gasification of CH tends to be near global pyrolysis, since at these conditions the temperature at the combustion zone is only 521°C, which is not much higher than the ignition temperature of C (400°C).
Highlights. (i) Biomass gasification for treatment of agroindustrial wastes is used. (ii) Syngas is generated through an updraft gasifier using coffee husk as fuel. (iii) Syngas HHV based on both air and steam as gasifying agents is improved.
Conflicts of Interest
The authors declare that they have no conflicts of interest.
The financial support from the internal financing grants of the Andes University and ECCI University is gratefully acknowledged.
References A. Williams, J. M. Jones, L. Ma, and M. Pourkashanian, “Pollutants from the combustion of solid biomass fuels,” Progress in Energy and Combustion Science, vol. 38, no. 2, pp. 113–137, 2012. View at Publisher · View at Google Scholar · View at ScopusR. Saidur, E. Abdelaziz, A. Demirbas, M. Hossain, and S. Mekhilef, “A review on biomass as a fuel for boilers,” Renewable and Sustainable Energy Reviews, vol. 15, no. 5, pp. 2262–2289, 2011. View at Publisher · View at Google Scholar International Coffee Organization, International Coffee Organization, Enero 2016, http://www.ico.org/trade_statistics.asp. Federacion Nacional de Cafeteros de Colombia, Federación Nacional de Cafeteros de Colombia, enero 2016, http://www.federaciondecafeteros.org/particulares/es/quienes_somos/119_estadisticas_historicas/. Institute of Nutrition of Central America and Panama, PULPA DE CAFÉ: composición, tecnología y utilización, Bogotá: CIID, 1978. J. L. De Oliveira, J. N. Da Silva, E. Graciosa Pereira, D. Oliveira Filho, and D. Rizzo Carvalho, “Characterization and mapping of waste from coffee and eucalyptus production in Brazil for thermochemical conversion of energy via gasification,” Renewable and Sustainable Energy Reviews, vol. 21, pp. 52–58, 2013. View at Publisher · View at Google Scholar · View at ScopusS. Priyadarsan, K. Annamalai, J. M. Sweeten, S. Mukhtar, and M. T. Holtzapple, “Fixed-bed gasification of feedlot manuere and poultry litter biomass,” Transactions of the ASAE, vol. 47, no. 5, pp. 1689–1696, 2004. View at Publisher · View at Google ScholarP. Basu, “Gasification Theory,” in Biomass Gasification, Pyrolysis and Torrefaction, pp. 199–248, Academic Press, 2ed edition, 2013. View at Publisher · View at Google ScholarG. Gordillo and K. Annamalai, “Adiabatic fixed bed gasification of dairy biomass with air and steam,” Fuel, vol. 89, no. 2, pp. 384–391, 2009. View at Publisher · View at Google Scholar · View at ScopusP. Basu, “Design of Biomass Gasifiers,” in Biomass Gasification and Pyrolysis, pp. 167–228, Academic Press, 2010. View at Publisher · View at Google ScholarG. Gordillo, K. Annamalai, and N. Carlin, “Adiabatic fixed-bed gasification of coal, dairy biomass, and feedlot biomass using an air-steam mixture as an oxidizing agent,” Renewable Energy, vol. 34, no. 12, pp. 2789–2797, 2009. View at Publisher · View at Google Scholar · View at ScopusN. Gao, A. Li, C. Quan, and F. Gao, “Hydrogen-rich gas production from biomass steam gasification in an updraft fixed-bed gasifier combined with a porous ceramic reformer,” International Journal of Hydrogen Energy, vol. 33, no. 20, pp. 5430–5438, 2008. View at Publisher · View at Google Scholar · View at ScopusP. Plis and R. K. Wilk, “Theoretical and experimental investigation of biomass gasification process in a fixed bed gasifier,” Energy, vol. 36, no. 6, pp. 3838–3845, 2008. View at Publisher · View at Google Scholar · View at ScopusJ. F. Vélez, F. Chejne, C. F. Valdés, E. J. Emery, and C. A. Londoño, “Co-gasification of Colombian coal and biomass in fluidized bed: an experimental study,” Fuel, vol. 88, no. 3, pp. 424–430, 2009. View at Publisher · View at Google Scholar · View at ScopusL. Wilson, G. R. John, C. F. Mhilu, W. Yang, and W. Blasiak, “Coffee husks gasification using high temperature air/steam agent,” Fuel Processing Technology, vol. 91, no. 10, pp. 1330–1337, 2010. View at Publisher · View at Google Scholar · View at ScopusS. Sun, Y. Zhao, F. Ling, and F. Su, “Experimental research on air staged cyclone gasification of rice husk,” Fuel Processing Technology, vol. 90, no. 4, pp. 465–471, 2009. View at Publisher · View at Google Scholar · View at ScopusG. Gordillo, Fixed bed counter-current low temperature gasification of dairy biomass and coal-daiy biomass blends usin air-steam as oxidizer [PhD dissertation], Texas A&M University, 2009. J. Bonilla, Estudio del efecto de relación equivalencia y la relación vapor combustible en la producción de gases combustibles por gasificación del cisco de café usando mezclas de aire-vapor para extracción parcial [MSc Disseratation], Universidad de los Andes, 2012. K. Zhang, J. Chang, Y. Guan, H. Chen, Y. Yang, and J. Jiang, “Lignocellulosic biomass gasification technology in China,” Renewable Energy, vol. 49, pp. 175–184, 2013. View at Publisher · View at Google ScholarC. A. Ibrahim Dincer, “Green methods for hydrogen production,” International Journal of Hydrogen, vol. 40, no. 34, pp. 11094–11111, 2012. View at Publisher · View at Google ScholarA. Gómez-Barea and B. Leckner, “Modeling of biomass gasification in fluidized bed,” Progress in Energy and Combustion Science, vol. 36, no. 4, pp. 444–509, 2010. View at Publisher · View at Google Scholar · View at ScopusP. Parthasarathy and K. S. Narayanan, “Hydrogen production from steam gasification of biomass: Influence of process parameters on hydrogen yield - A review,” Renewable Energy, vol. 66, pp. 570–579, 2014. View at Publisher · View at Google Scholar · View at ScopusH. L. Chum and R. P. Overend, “Biomass and renewable fuels,” Fuel Processing Technology, vol. 71, no. 1-3, pp. 187–195, 2001. View at Publisher · View at Google Scholar · View at ScopusS. S. Thanapal, K. Annamalai, J. M. Sweeten, and G. Gordillo, “Fixed bed gasification of dairy biomass with enriched air mixture,” Applied Energy, vol. 97, pp. 525–531, 2012. View at Publisher · View at Google Scholar · View at ScopusS. Sharma and P. N. Sheth, “Air-steam biomass gasification: Experiments, modeling and simulation,” Energy Conversion and Management, vol. 110, pp. 307–318, 2016. View at Publisher · View at Google Scholar · View at ScopusE. Balu, U. Lee, and J. N. Chung, “High temperature steam gasification of woody biomass - A combined experimental and mathematical modeling approach,” International Journal of Hydrogen Energy, vol. 40, no. 41, pp. 14104–14115, 2015. View at Publisher · View at Google Scholar · View at ScopusG. Gordillo and C. Rodriguez, “Adiabatic gasification and pyrolysis of coffee husk using air-steam for partial oxidation,” Journal of Combustion, vol. 2011, Article ID 303168, 2011. View at Publisher · View at Google Scholar · View at Scopus