Deepak Kumar Ojhaa and
R. Vinu*ab
aDepartment of Chemical Engineering, Indian Institute of Technology Madras, Chennai-600036, India. E-mail: vinu@iitm.ac.in; Tel: +91-44-2257-4187
bNational Center for Combustion Research and Development, Indian Institute of Technology Madras, Chennai-600036, India
First published on 29th July 2015
In this study, the production of high quality biofuel intermediates via fast co-pyrolysis of cellulose and polypropylene (PP) is investigated. Fast co-pyrolysis experiments were performed in a Pyroprobe® reactor and the generated vapors were analyzed using a gas chromatograph-mass spectrometer for the composition of pyrolysates, and Fourier transform infrared spectrometer for the time evolution of the key functional groups. The effects of cellulose : PP mass ratio (100:0, 75:25, 50:50, 25:75, 0:100) and temperature (500–800 °C) on bio-oil composition, carbon number distribution of the products, higher heating value of the products, and temporal evolution of O–H, C–O, –CH2–, CO2 and CO groups were evaluated. Formation of long chain alcohols in the carbon number range of C8–C20 was observed as a result of the interaction of cellulose and PP. Feed composition played a decisive role in the formation of alcohols and hydrocarbons. A maximum of ca. 36% alcohols and 45% hydrocarbons were obtained from PP-rich mixture at 600 °C. The yield of char decreased and that of the aromatic hydrocarbons increased with pyrolysis temperature. Significant improvement in the heating value of the products was observed when PP was blended with cellulose. Importantly, the calculated heating values correlated well with the cumulative content of alcohols, aliphatic and aromatic hydrocarbons. The addition of PP to cellulose significantly decreased the time taken for completion of pyrolysis. Based on the product distribution, hydroxyl, hydrogen and methyl abstraction were found to be the dominant reactions involved in the transformations.
Bio-oil upgradation to drop-in fuels and intermediates is achieved by two common techniques, namely, catalytic upgrading and hydrodeoxygenation. Catalytic upgrading involves fast pyrolyzing the feedstock in presence of catalysts such as zeolites, transition metal oxides or mesoporous materials.1,6 Hydrodeoxygenation (HDO) involves removal of oxygen from the feedstock by passing hydrogen gas at high pressures in presence of hydrotreating catalysts such as bifunctional Co–Mo/Al2O3.7,8 This upgrading technique is capable of removing more than 90% of oxygen in the feedstock to produce gasoline and diesel range fuels. However, the process is highly hydrogen intensive and has shortcomings of catalyst deactivation. Furthermore, if the operating conditions are not optimized properly, the competing polymerization reaction of dehydrated intermediates leads to the formation of high molecular weight compounds and char/coke.9
Co-feeding hydrogen-rich thermoplastic polymers along with oxygen-rich biomass is a potential strategy to improve the quality of bio-oil, especially the H/O ratio. This also paves way for a better utilization of waste plastics that constitute a major fraction of municipal solid wastes.10 Even partial removal of oxygen in the bio-oil can significantly reduce the consumption of hydrogen in the HDO step. Besides, this also improves the stability of bio-oil. The presence of olefinic polymers is thought to induce hydrogen abstraction reactions between the long chain polymer species and free radicals produced from biomass intermediates.11 The elementary reactions occurring in the melt phase during fast pyrolysis include a number of competing free radical, ionic and concerted reactions of cellulose, hemicellulose, lignin, ash and polymeric species. While olefinic polymers are well known to decompose via a cascade of free radical reactions,12 the specific reactions involved in the transformation of biomass components are largely unclear.13 Therefore, it is very important to characterize the co-pyrolysis behavior of pure components of biomass and polymers using various analytical techniques.
Co-pyrolysis of biomasses, such as cellulose, xylan, lignin, switch grass, pine, beech and spruce woods, with polymers, such as polystyrene, polyethylenes, polypropylene (PP), poly(ethylene terephthalate), poly(vinyl chloride) (PVC) and tyres is reported in the literature.10,11,14–24 In a series of studies, Sharypov and co-workers11,14–16 evaluated the effects of feed composition and additives on the product yield and quality during co-pyrolysis of biomass and polymers in a rotating autoclave. It was found that the product evolution was additive when biomass composition in the feed was 50–100%, while higher plastic content made the product evolution non-additive. The higher liquid and lower char yields were attributed to the hydrogen transfer reaction from polyolefins to biomass radicals that tend to stabilize the primary products from cellulose degradation. Mullen and co-workers21,22 studied catalytic fast co-pyrolysis of biomass with polymers using HZSM-5, and observed a synergism in the formation of aromatic compounds like toluene, ethylbenzene, xylenes and naphthalenes via Diels–Alder reactions. In another recent study of fast co-pyrolysis of biomass components with PVC, the interactions were found to decrease the HCl yield and improve tar yield.24 Recently, we evaluated the kinetics of slow co-pyrolysis of cellulose and PP using thermogravimetric analyzer, and showed that the interactions between the primary volatiles from cellulose with activated PP decrease the apparent activation energy of the process.10 While the existing studies demonstrate the positive effects of co-pyrolysis on overall product spectrum, the exact mechanism and interactions between biomass and polymers are largely unclear owing to the presence of a large number of competing reactions. Moreover, the effect of co-pyrolysis on pyrolysis time scales is also not known.
The present work aims to unravel the key interactions between cellulose and PP during non-catalytic fast co-pyrolysis using analytical pyrolyser (Py) coupled with high resolution gas chromatograph-mass spectrometer (GC/MS) and Fourier transform infrared spectroscopy (FT-IR). The effects of feed composition and temperature on the evolution of pyrolysates are evaluated. The quality of the pyrolysates obtained under different conditions is assessed by evaluating the carbon number distribution and heating value. The evolution of key functional groups at short time scales during fast co-pyrolysis is studied using Py-FT-IR, and plausible reaction mechanism is proposed.
Fig. 1 Composition of pyrolysates when cellulose, polypropylene and their mixtures of different compositions were pyrolyzed at 500 °C. |
In order to understand if the product formation is linear with composition of cellulose:PP, the experimental product compositions are compared with the calculated ones as shown in Table 1. The calculated product composition in the case of mixtures is based on the experimental product yields from fast pyrolysis of pure cellulose and PP according to the formula, Ycalc.mix = XcelluloseYexpt.cellulose + XPPYexpt.PP. Y corresponds to the yield of a particular organic compound, while Xcellulose and XPP denote the mass composition of cellulose and PP in the feed. It is clear that the formation of hydrocarbons follows the calculated composition up to C:PP ratio of 50:50. All other products deviate significantly from the calculated values, suggesting that these compounds are indeed involved in the interactions leading to the formation of new products, i.e. alcohols. Except alcohols and char, the experimental compositions of other product groups, such as anhydrosugars, carbonyl compounds and furans, are lower than that of the calculated values. Importantly, the yield of alcohols increases with increase in PP content in the feed. From Table S1 (in ESI†), it is evident that a majority of these alcohols contain more than 7 carbon atoms and are linear, branched or cyclic. The hydrocarbon backbone of a number of these alcohols also mimics the products from pure PP pyrolysis. In order to evaluate the positive effect of co-pyrolysis on the reduction of oxygen content in the pyrolysates, the total oxygen present in the condensable fraction was evaluated based on GC/MS data of product composition. This was compared with the oxygen present in the feed mixtures. As PP does not contain oxygen, the oxygen content in the mixture was calculated only based on cellulose [(–C6H10O5–)n]. The C, H and O content in the feed mixtures and bio-oils obtained at 500 °C are tabulated in Table S7 (in ESI†). The extent of deoxygenation was calculated as the ratio of difference between oxygen content in feed and that in bio-oil to oxygen content in feed. The extent of deoxygenation achieved in the pyrolysates was ca. 40% for pure cellulose, while it was 67%, 73.5% and 62% for cellulose:PP mixtures of 75:25, 50:50 and 25:75 mass ratios, respectively. It is evident that the presence of optimal amount of cellulose is important to achieve high deoxygenation via dehydration, decarboxylation and decarbonylation reactions. PP rich mixture inherently contains lesser amount of oxygen, and the observed trend indicates that favorable interactions in the form of oxygen removal reactions occur in the equal composition mixture of cellulose and PP. The magnitude of deoxygenation obtained in this work is comparable with the literature. Sharypov et al.11 observed nearly 90% deoxygenation in the heavy liquid fractions obtained from pyrolysis of mixtures of pine wood, beech wood and lignin with PP in a high pressure autoclave.
Products | Feed composition | |||||||
---|---|---|---|---|---|---|---|---|
C:PP 100:0 | C:PP 75:25 | C:PP 50:50 | C:PP 25:75 | C:PP 0:100 | ||||
Expt. | Expt. | Calc. | Expt. | Calc. | Expt. | Calc. | Expt. | |
a The calculated composition was evaluated using the formula given by Ycalc.mix = XcelluloseYexpt.cellulose + XPPYexpt.PP. | ||||||||
Alcohols | 6.95 | 22.73 | 5.21 | 27.81 | 3.48 | 30.87 | 1.74 | 0 |
Hydrocarbons | 0.67 | 28.23 | 23.56 | 40.21 | 46.44 | 43.65 | 69.33 | 92.20 |
Anhydrosugars | 17.36 | 7.11 | 13.02 | 2.92 | 8.68 | 1.70 | 4.34 | 0 |
Aldehydes/ketones | 23.20 | 10.63 | 17.40 | 5.80 | 11.60 | 1.83 | 5.80 | 0 |
Furans | 27.89 | 9.92 | 20.92 | 6.20 | 13.95 | 1.76 | 6.97 | 0 |
Char | 5.67 | 11.29 | 6.20 | 14.32 | 6.73 | 13.28 | 7.27 | 7.80 |
Fig. 2 Effect of temperature on composition of major products formed during fast co-pyrolysis of C:PP of different compositions. |
With increase in temperature, the formation of oxygenated compounds such as anhydrosugars, furan derivatives and carbonyl compounds decreased for a majority of the mixture compositions. There was no significant variation of carboxylic acids and esters with temperature, and their yield was 1–2% for all the mixtures. A clear decrease in yield of anhydrosugars with temperature was observed for cellulose:PP of 75:25, while their formation increased at higher temperatures for 50:50 and 25:75 mixture compositions. Nevertheless, the overall yield of anhydrosugars was less than 3% for these mixtures owing to the low content of cellulose. Hydroxy- and methyl-substituted pyranones were also grouped under anhydrosugars. 1,4:3,6-Dianhydro glucopyranose was the major anhydrosugar observed at all temperatures. A similar variation was also observed for furans and their derivatives. For the equal composition mixture, furans production continuously increased with temperature that the yield was doubled at 800 °C. The formation of furans is proposed to occur via ring closing of sugars followed by dehydration reactions.13,39 Importantly, aldol condensation of lighter oxygenates from cellulose pyrolysis such as acetaldehyde and glycolaldehyde can lead to the formation of tetraose sugars that act as precursors for furans.40 The yield of aldehydes and ketones varied in the range of 4–8% for 75:25 and 50:50 mixtures, while their production was less than 3% for 25:75 mixture. Importantly, the formation of benzene derivatives (monoaromatics), and polyaromatic hydrocarbons (PAHs) increased with temperature. Majority of the monoaromatics included benzene, toluene and xylene (BTX), styrene, ethyl benzene and ethyl methyl benzene, while PAHs included naphthalene, alkyl naphthalenes, acenaphthylene, indene, methyl indene, anthracene, and fluorene among other minor derivatives of the above compounds. Significant production of the above aromatics occurred only at 700 and 800 °C. Very high yields of monoaromatics (26.5%) and PAHs (24.76%) were observed at 800 °C for the equal composition mixture, while their yield was lesser for both cellulose and PP-rich mixtures.
From Fig. 2, it is evident that there is a drastic decrease in alcohol and hydrocarbon yields at 800 °C for the equal composition mixture, which is also significantly lower than that for the other mixtures at the same temperature. This can be correlated with the formation of aromatic hydrocarbons. Linear hydrocarbon end-chain radicals from PP can form aromatics via 1,6-cyclization, followed by β-scission and hydrogen abstraction reactions.12 Benzene formation is proposed to occur at high pyrolysis temperatures from linear alkenes via cyclization reaction.41 C2–C6 alkenes are formed at high temperatures (700–800 °C) via end-chain β-scission and hydrogen abstraction reactions.32,42 The formation of aromatics such as BTX during catalytic fast co-pyrolysis of cellulose and PP is shown to occur via Diels–Alder cycloaddition reaction between a furan derivative from cellulose and C2/C3 alkene from PP.22 Similarly, the reaction of alkenes with alcohol fragments and C2–C3 carbonyl and carboxylic acids can result in the formation of phenolic compounds. This is substantiated by the significant production of phenolic compounds (ca. 2%) from 50:50 mixture at 800 °C. Owing to the optimum formation of cellulose and PP derived small fragments from the equal composition mixture, the yields of aromatics, PAHs, and char are high.
Fig. 3 Effect of temperature and cellulose:PP composition on carbon number distribution of the major products in bio-oil. |
Scheme 1 Proposed mechanism for the formation of alcohols during fast co-pyrolysis of cellulose and PP. |
In order to assess the energy content of the condensates from co-pyrolysis, higher heating value (HHV) of the condensable fraction was evaluated using the Lloyd and Davenport's formula given by, HHV (MJ kg−1) = −0.3578[%C] − 1.1357[%H] + 0.0845[%O] − 0.0594[%N] − 0.1119[%S].43 The percentage of C, H and O were evaluated by using the GC/MS product composition data. While there are a number of empirical formulae available in the literature to calculate HHV of a variety of feedstocks,44 we chose this formula after testing its validity for the feed mixtures. The HHVs of the feed mixtures determined using a bomb calorimeter are listed in Table S9 (in ESI†). Cellulose has a low heating value (15.54 MJ kg−1), while PP has a very high heating value (46.47 MJ kg−1). The HHVs of the mixtures increase linearly with PP content in the feed. The HHVs calculated by Lloyd and Davenport's formula for the feed mixtures matched well with experimental data. As expected, the HHV of cellulose derived bio-oil was 21.7 MJ kg−1, while that from pure PP was 43.23 MJ kg−1. HHVs of the pyrolysates from the mixtures at different temperatures varied in the range of 36–41 MJ kg−1 (Fig. 4). This is due to long chain hydrocarbons and alcohols that contribute significantly to the H content in the oil fraction, and hence, the heating value. The energy densification ratio, defined as HHVoil/HHVfeed, varied in the range of 1 to 1.5 for the oils derived from the mixtures. As alcohols, hydrocarbons and benzene derivatives constitute a major fraction (>50%) of the bio-oil components, they are expected to contribute more to the heating value, especially for the fast pyrolysis of mixtures. Therefore, the sum of yields of these components obtained from various experiments were plotted against calculated HHVs. A striking linear correlation is evident from Fig. 4, which shows that the major products contribute to an effective increase in heating value of the oil. While the recent studies on co-pyrolysis of biomass and polymers have shown that the production of aromatics can be improved by using catalysts such as zeolites,19–23 our study shows that non-catalytic co-pyrolysis is a promising upstream processing technique to improve the quality of the bio-oil. Importantly, high yield of C8–C20 alcohols and C6–C15 hydrocarbons, that are valuable as gasoline range compounds are produced during fast co-pyrolysis. The co-pyrolysis bio-oil can then be subjected to catalytic HDO with possibly low hydrogen load.
Fig. 6(a)–(e) depict the time evolution of major component vibrations for cellulose, PP and the mixtures. For cellulose pyrolysis, the intensity of carbonyl and primary alcohol vibrations are higher than other functional groups, suggesting that CO and –OH groups present in C2–C4 alcohols, aldehydes, ketones, furan derivatives like furfural, 5-hydroxymethyl furfural and furanones, carboxylic acids, and anhydrosugars such as pyranones and levoglucosenone, are produced in high amounts. This is also in good agreement with the products identified by GC/MS (Tables S1–S6 in ESI†). Importantly, the maximum production of the major products occurs at 12–14 s. Except carbonyl vibration, the intensity of other functional groups are steady after 16 s, suggesting that a majority of the products bearing alcohol functional groups evolve even at much longer timescales (30–40 s). These might include C2–C3 oxygenates such as hydroxy actaldehyde (glycolaldehyde), hydroxy acetone (acetol), oxo acetic acid (glyoxylic acid) and 2-oxo propanoic acid (pyruvic acid), which are obtained in significant amounts during cellulose fast pyrolysis at 500 °C (Tables S2 and S4 in ESI†). This shows that during cellulose fast pyrolysis, dehydration of pyranose units along with cellulose chain initiation and depropagation are the dominant reactions13,39 in the initial time periods, while the formation of C2–C3 oxygenates via secondary transformation of dehydrated C4–C6 sugars via retro-Diels–Alder and retro-aldol reactions13,39 occur at longer timescales.
The addition of PP to cellulose results in the formation of the same functional groups, albeit at very different intensities and pyrolysis times. As depicted in Fig. 6(b), the addition of 25% of PP to cellulose results in decrease in intensity of carbonyl vibration and a concomitant increase in –CH2– vibration arising from the hydrocarbon backbone. Unlike pure cellulose fast pyrolysis, all the peaks tend to decrease after reaching maxima signifying the decrease in concentration of the functional groups. This shows that the incorporation of PP tends to accelerate the completion of pyrolysis. The profile of –CH2– vibration exhibits two humps, one at 15 s and another at 20 s. The earlier hump matches with the time corresponding to maximum evolution of primary alcohols, indicating that long chain alcohols are formed as a result of hydroxyl radical interaction between cellulose and PP. The second hump is expected to correspond to the evolution of hydrocarbons from PP. An increase in PP composition in the mixture leads to interesting changes in the evolution of products. From Fig. 6(c) and (d), it is clear that the time taken for maximum production of various functional groups decreases significantly to 10 s, and all the functional group peak heights decrease to zero, signifying faster completion of pyrolysis compared to cellulose and cellulose-rich mixture. Based on the intensity of the vibrations, the functional groups can be arranged as follows: –CH2– (hydrocarbons) > O–H (water + alcohols) > CO2 > CO (carbonyl/acids) > C–O (primary alcohols). The profiles of methylene stretching vibration for equal composition (50:50) and PP-rich (25:75) mixtures are very similar to that for pure PP pyrolysis (Fig. 6(e)). It can be observed that the intensity of O–H stretching vibration is higher than C–O stretching vibration exhibited by primary alcohols, especially when PP content is equal or higher in the mixture. This suggests that increasing the PP content in the mixture leads to higher extent of dehydration via hydroxyl and hydrogen shift reactions. It can hence be concluded that besides improving the quality of the condensable fraction in terms of the production of long chain alcohols and hydrocarbons, co-pyrolyzing PP with cellulose decreases the time for completion of the reaction significantly. This will lead to better conversion of the feedstock in larger scale reactors.
Fig. 6(f) depicts the concentration profiles of CO and CH4 measured using an online gas analyzer. The timescales corresponding to the evolution of these gases do not exactly match with the timescale of the condensates owing to the residence time of the gases in the tubing leading to the gas analyzer. Nevertheless, the CH4 evolution is similar to the trend exhibited by –CH2– vibration at different cellulose:PP compositions. A clear shift in maximum concentration of CH4 to shorter time periods is observed for equal composition and PP-rich mixtures, which reconfirms the trends observed in FT-IR profiles. Thus alcohol and hydrocarbon production occur simultaneously at short timescales during co-pyrolysis. CO evolution starts even before the evolution of CH4, which shows that cellulose begins to pyrolyze via concerted reactions even before free radical formation from PP could occur. CO evolution is high for cellulose-rich mixtures, and it increases with 25% addition of PP. It is also worthwhile to note that the intensity of CO2 vibration increases significantly for 50:50 and 75:25 mixtures compared to that for cellulose-rich mixtures (Fig. 6(c) and (d)). These results show that deoxygenation occurs predominantly via decarbonylation and decarboxylation during co-pyrolysis. An ensemble of the above observations suggest that co-pyrolyzing biomass with polymers is a promising option to improve deoxygenation, and hence, the quality of bio-oil. Importantly, this is the first work to show the time evolution of key functional groups during fast co-pyrolysis and evaluate the effects of cellulose:PP composition on reaction timescales and provide qualitative insights on product formation mechanisms and interactions between cellulose and PP. More rigorous studies on characterization and stability of bio-oil from fast co-pyrolysis of actual biomass and commercial plastics will aid in commercialization of this process.
Footnote |
† Electronic supplementary information (ESI) available. See DOI: 10.1039/c5ra10820a |
This journal is © The Royal Society of Chemistry 2015 |