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220    Cha pte r  Se v e n

               Because of their amorphous structure, hemicelluloses have lower
               thermal stability than cellulose. Their thermal degradation starts at
               temperatures as low as 200°C. The yields of furfural increase when
               the substrate is impregnated with acid catalysts (Radlein et al. 1991a,
               1991b).

               Lignin
               Thermal degradation of lignin occurs over a wide range of tempera-
               tures (200 to 600°C), resulting in the formation of monomeric phenols,
               guaiacols and syringols, formic acid, formaldehyde, methanol, carbon
               dioxide, and water. Demethoxylation of lignin is the source of meth-
               anol. In general, the thermal degradation of lignin can be described
               by a competitive mechanism involving depolymerization and
               condensation/carbonization reactions as suggested by Kawamoto
               et al. (2007b). During fast pyrolysis, most of the lignin is converted
               into monomers, dimers, and trimers. The dimers and trimers are
               known as pyrolytic lignin. Many of these dimers and trimers are
               released in the form of aerosols (Garcia-Pérez et al. 2008).


          7.4 Single-Particle Models
               Understanding how the thermal degradation of individual biomass
               particles proceeds is critical to design and to operate more efficient
               pyrolysis reactors. The conversion of a single biomass particle is con-
               trolled by the physicochemical properties and dimensions of biomass
               particles as well as by the reaction conditions (reactor temperature,
               reacting environment, external heat transfer coefficient). The residence
               time of biomass particles inside a pyrolysis reactor needed to achieve
               complete conversion will depend on the devolatilization and heating
               rates. Total conversion time can be calculated by single-particle mod-
               els. The values of total devolatilization time for small biomass particles
               (diameter less than 2 mm) in fluidized-bed reactors reported in the
               literature are between 10 and 70 s (Kumar et al. 2006).
                   Many models have been developed over the last 60 years to
               describe the thermal degradation of single biomass particles. In general,
               it is accepted that for particles with length-to-diameter ratio smaller
               than 3 should be described by two-dimensional models. One-
               dimensional models should be used when describing biomass parti-
               cles with length-to-diameter ratios larger than 3. Excellent reviews on
               the single-particle models used to calculate biomass devolatilization
               time can be found elsewhere (Kersten et al. 2005, Di Blasi 2008).
                   When designing a pyrolysis reactor it is very important to distin-
               guish between the reactor temperature and the temperature at which
               primary thermochemical reactions occur. The reactor temperature is
               usually higher than the particle temperature, which controls the reac-
               tion rate of primary thermochemical reactions (Bridgwater et al. 1999).
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