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62                      Refining Biomass Residues for Sustainable Energy and Bioproducts


          Table 3.2 Microbial studies for PHA production using waste as a substrate.
          Organism          Carbon source      PHA           References
                                               concentration
                                               (g/L)
          Burkholderia      Sugarcane bagasse  2.73          Silva et al. (2004)
            sacchari IPT 101  hydrolysate
          Ralstonia eutropha  Waste biomass    11.42         Saratale and Oh
            ATCC 17699        hydrolysate                      (2015)
          Bacillus cereus M5  Molasses         0.13          Yilmaz and Beyatli
                                                               (2005)
          Serratia sp.      50% Wastewater and  0.3368       Gupta et al. (2017)
            ISTVKR1           0.5% glucose
          Pandoraea sp.     Lignin derivative  0.409         Kumar et al. (2017)
            ISTKB
          Serratia sp.      Municipal secondary  0.605       Kumar et al. (2018)
                              wastewater sludge
          Serratia sp.      1% glucose and     0.421         Kumar et al.
                              20 mM bicarbonate                (2016a,b)
          Cupriavidus necator  Waste potato starch  94       Haas et al. (2008)
            NCIMB 11599
          Pseudomonas       Sugarcane liquor   22.4          Jiang et al. (2008)
            fluorescens A2a5
          Pseudomonas       Hydrolyzed whey    1.27          Koller et al. (2008)
            hydrogenovora
          C. necator DSM    Crude glycerol     38.5          Cavalheiro et al.
            545                                                (2009)
          Ralstonia eutrophus  Fruit and       1.13          Ganzeveld et al.
                              vegetable waste                  (1999)




         phosphorus (Anderson and Dawes, 1990). When limiting nutrient source is
         restored, PHAs are reduced by an intracellular depolymerase and then processed
         as a source of carbon and energy and also the number of microbes will increase
         (Taidi et al., 1994).
           On the basis of the number of carbon atoms, PHAs are classified into the
         following groups that is, SCL-PHAs, MCL-PHAs, or LCL-PHAs (Maheshwari
         et al., 2018). Physical properties are depending upon the functional group and
         the length of the side chain. The SCL-PHAs are stiff, crystalline, and brittle
         polymers with a low glass transition temperature and high melting point while
         MCL-PHAs have a low melting point, tensile strength, and crystallinity. The
         most abundant family member of PHA is poly(3-HB) (P(3HB)). By using
         various substrates within a cofeeding system, copolymers of polyhydroxybutyrate
         (PHB) can be found like polymers comprising 4-HB or hydroxyvalerate (3HV)
         monomers.
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