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Sweet sorghum: a potential resource for bioenergy production      233



           biomass is subjected to temperatures below 900 C with deprived environment of
           oxygen to form a carbon-rich solid material. The yield of biochar in fast pyrolysis,
           gasification, torrefaction, hydrothermal carbonization, and slow pyrolysis is B12%,
           B10%, B80%, 50% 80%, and B35%, respectively (Godlewska et al., 2017;
           Kambo and Dutta, 2015; Zhang et al., 2019b). In recent times, characteristics, such
           as large surface area, high degree of porosity, and the presence of functional groups
           on the surface, have drawn much attention to biochar as a potential solution to
           resolve environmental management problems (Zhang et al., 2019b). Biochar have
           been utilized for the soil remediation, GHG reduction (including CO 2 capturing),
           efficient sorbent material, and energy production as a solid fuel act as a catalyst
           and high C-rich compositing material (Huang et al., 2015; Qambrani et al., 2017;
           Zhang et al., 2019b).
              Biochar of sorghum biomass contains 14.7% of volatile matter, 62.8% of fixed
           carbon, and 18.7% of ash content, which is obtained from fast-pyrolysis process. In
           the ultimate analysis, C, H, N, and O contents are 69.0%, 2.7%, 0.59%, and 27.6%
           of total weight percentage, respectively. Heating values, that is, HHV and LHVs,
           are 23.11 and 22.51 MJ/kg, respectively, that is higher as compared to that of sor-
           ghum biomass. The morphology of biochar shows that it is highly porous in nature
           which contains 1 20 μm of regular pores. It can be exploited to produce activated
           carbon as it contains higher amount of C. In addition, it can be applied for the
           remediation of metal ions, pesticides, polycyclic aromatic hydrocarbons, etc.
           (Soudek et al., 2017; Yin et al., 2013).
              Various researchers have found that biochar application in soil fertilization, car-
           bon sequestration, plant growth, and the improvement of soil structure has resulted
           in improved sorghum growth and yield under sandy desert soils. The sorghum crop
           yield was found to increase when biochar was applied at the rate of 22 Mg/ha
           (Laghari et al., 2015). Similarly, Blackwell et al. (2015) observed that addition of
           biochar and biochar mineral complex enhanced the colonization of mycorrhiza
           and nutrition in wheat and sorghum. Moreover, sorghum biochar has been used to
           increase the biomass of winter wheat (Sigua et al., 2015). In order to remove toxic-
           ity of Cd, Cu, and Pb, sorghum seed germination was increased in the presence of
           biochar (Soudek et al., 2017).

           10.4.4 Value-added products

           Sorghum bagasse and sorghum syrup have major application in the production of
           bioethanol, biogas, biochar, biooil, and syngas. However, other coproducts, such as
           processed bagasse, steam, foam, and forth, obtained during the syrup or ethanol
           production and waste vinasse generated during the dewatering process can be fur-
           ther utilized for the energy production and ruminant or poultry feed (de Resende
           et al., 2006; Srinivasa Rao et al., 2012; Ray et al., 2019).
              The processed or discarded sorghum biomass can be utilized for the production
           of solid biofuels (briquettes). Gross and net calorific values of briquettes based on
           sweet sorghum biomass were 18.9 and 17.7 MJ/kg, respectively. Calorific values of
           sorghum briquettes were comparable with the sawdust briquettes. Sorghum residual
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