Investigations into the characteristics of oils produced from co-pyrolysis of biomass and tire
Introduction
Many researchers are widely being concerned by environmental-friendly disposal and utilization of waste tire and biomass as a resource [1], [2], [3], [4], [5]. Especially, with the gradual decrease of fossil reserves these recycled matters are firstly considered as an alterative resource of energies and chemicals [6], [7]. Although the bio-oil obtained by pyrolyzing biomass possibly becomes a type of potential transporting fuel, some problems such as higher oxygen content, lower high heat value (HHV), lower volatile and delayed ignition time in engine severely hinder its use in practice [8], [9]. It is hence necessary to study how to upgrade the bio-oil. At present, the following pathways were used. The first one was a high pressure hydrogen processing and catalytic cracking [10]. Al-MCM-41 as a catalyst pyrolyzing vapors of spruce wood could lower the yield of phenols with higher molecular mass [11], and sulfided Co–Mo–P as a catalyst could obviously reduce oxygen content in the oil in an autoclave under hydrogen pressure of 2.0 MPa [12]. A steam reforming of oil for the production of hydrogen with catalyst was also studied [13]. Using a high pressure in the system for upgrading the bio-oil not only increased the cost for the production of the oil, but also enhanced the demand for the equipment. The second way was a co-pyrolysis for the mixture of synthetic polymers and biomass [14], [15], [16], [17], [18], which were converted into the liquids with conversation yield of 78 wt.% to 79 wt.% under a nitrogen atmosphere [17]. Another way was esterification for the pyrolysis oil with a high boiling alcohol in the presence of acid catalyst under reduced pressure [19], [20]. In this process, only partial compounds were esterified and consumed a great deal of energy. Emulsion of pyrolysis oil and diesel with a surface active agent was also studied [21]. However, use of the surface active agent increased the cost of the oil.
It is well-known that the result of the ultimate analysis for biomass has a strong function with the types used. The C content for the most biomass is between 47 wt.% and 51 wt.%, whereas the O content is between 42 wt.% and 46 wt.%, leading to very high O content in the pyrolysis oil. In contrast, the C content is very high and O content is very low in the waste tire, whose corresponding content is about 84 wt.% and 1.5 wt.% respectively. If biomass and tire are co-pyrolyzed, C, O and H contents of the feedstock will be balanced. Also, it is conducive to change the C, O and H contents in the oil. In addition, a great deal of free radical species produced by the pyrolysis of biomass possibly destroy or suppress the formation of some long chain hydrocarbon compounds and undesired matters like PAHs from the pyrolysis of tire alone. Although there are some data about the oil from wood biomass and some synthetic polymers like polypropylene, there are less data about the oil from the mixture of biomass and tire because tire property is completely different from polypropylene. In the previous study [14], we reported the influence of different pyrolysis temperatures on the liquid yield and limonene content in the co-pyrolysis oil. In this paper, the thermal behavior of feedstock and oil properties like molecular weight distribution, PAHs and elemental contents with and without catalysts were emphatically investigated.
Section snippets
Material
The particle size of tire powder from Qing Dao Green Leaf Ltd. was less than 165 µm. Sawdust, which came from the timber industry, was powdered, screened (198–350 µm) and dried for 4–5 h at 105 °C before the experiment. The elemental composition and proximate analysis of the materials are shown in Table 1. The characteristics of the molecular sieve SBA-15, MCM-41 and HZSM-5, which were supplied by Chuang Chun New Technology Company (China), are listed in Table 2. Zinc oxide, dichloromethane and
Thermal analysis of the mixture of biomass and waste tire
The decomposition profiles of the feedstock are given in Fig. 2. It is seen that the start temperature of mass loss for sawdust, tire and the mixture of 60 wt.% sawdust with 40 wt.% tire (S60T40) occurs at 275.3 °C, 341.7 °C, 292.8 °C, respectively. The corresponding end temperature of mass loss is at 389.8 °C, 480.7 °C, 394.1 °C, respectively. The temperature of the mass loss maximum rate occurs at 359.8 °C, 384.3 °C and 361.6 °C in sequence. It is noticed that the difference of the
Conclusions
Co-pyrolysis of sawdust and tire can inhibit the formation of PAHs produced by pyrolysis tire alone. When sawdust mass accounts for 60% in the mixture, the amount of PAHs in the oil is the lowest. In comparison with the H/C ratio of the T0, the H/C ratio of the oil from co-pyrolysis increases. For the T0 and T40, the ratio of H/C is 1.33 and 1.45, respectively. The increment of H/C ratio is the result of hydrogen transfer among the pyrolysis vapors of tire and sawdust. Meso-pore molecular sieve
Acknowledgments
The authors are very grateful for the financial support from the National Natural Science Foundation of China (NSFC, No.50576062) and Shanxi Province Natural Science Fund in China “No.2006011020”.
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