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44    Lignocellulosic Biomass to Liquid Biofuels


          deactivated. Therefore improving the enzyme stability and activity is cru-
          cial to this integrated process.
             Application of ILs for biomass pretreatment has provided a new path
          for effective utilization of biomass. However, there are still many chal-
          lenges for industrialization of IL-based pretreatment. The most important
          challenge is the high cost of ILs, and thus to find economical solutions for
          the reuse and recycle of ILs is of great importance. How to eliminate the
          toxicity of the residual ILs to cellulases and microorganisms is also
          important.


          2.4 Biological pretreatment
          Biological pretreatment refers to using microorganisms or enzymes to pre-
          treat various lignocellulosic materials prior to enzymatic hydrolysis of
          polysaccharide [1]. The primary microorganisms used mainly include
          white- (e.g., Phanerochaete chrysosporium and Ceriporia lacerata), brown-
          (e.g., Serpula lacrymans and Coniophora puteana), and soft-rot (e.g.,
          Paecilomyces sp. and Cadophora spp.) fungi as well as bacteria (e.g., Bacillus
          circulans and Sphingomonas paucimobilis) to degrade lignin, partially hydro-
          lyze hemicelluloses, and reduce DP of cellulose [4]. It was reported that
          white-rot fungi are the most widely used and effective for biological pre-
          treatment [7]. The advantages of biological pretreatment are low energy
          requirement, no or little chemicals requirement, mild pretreatment condi-
          tions, and little environmental pollution. However, the primary disadvan-
          tage of biological pretreatment is the low efficiency [7]. Different fungi or
          bacteria secrete different enzyme systems and have different effects on pre-
          treatment. White- and soft-rot fungi secrete enzyme systems comprising
          xylanase, lignin peroxidases, polyphenol oxidases, manganese-dependent
          peroxidases, and laccases as the main compositions and can catalyze the
          degradation of lignin and hemicellulose [4].
             Sindhu et al. investigated biological pretreatment of paddy straw with
          white-fungus (Trametes hirsuta) and compared with SE pretreatment at
          121°C. The results indicated that biological pretreatment had higher lig-
          nin removal than SE. The highest saccharification efficiency observed after
          24 h for biological pretreatment (76.5%) was also somewhat higher than
          that of steam pretreatment (74.1%), with a maximum production of sugar
          (52.91 g/L) observed for biologically pretreated biomass at 10% glucan
          loading after 24 h enzymatic hydrolysis [2]. Gao et al. compared Trametes
          versicolor 52J (TV52J), T. versicolor m4D (TVm4D), and P. chrysosporium to
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