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Agroindustry wastes: biofuels and biomaterials feedstocks for sustainable rural development  373



                               Acid forming   Methane forming
                                organisms       organisms

                                                          Methane
                         Organic         Volatile           and
                          waste           acids
                                                        carbon dioxide
                                 Phase 1         Phase 2
                                  Acid           Methane
                               fermentation    fermentation
           Figure 16.3 Two-step microbial fermentation process for methane production (Obi et al.,
           2016).
           bacteria. Then, these organic acids are consumed by methanogenic organisms to
           yield gas that has high methane content (Obi et al., 2016). The typical composition
           of the produced gas has 50% 70% of methane, 25% 45% of CO 2 , 0.5% 3% of
           N 2 ,1% 10% of H 2 with little amount of H 2 S, whose heating value is in the range
                         3
           of 18 25 MJ/m (Timbers and Downing, 1977). The major disadvantage of the
           digestion system is high cost. Further, the explosive properties of the methane gas
           make working condition difficult for operators. However, the advantages of the
           anaerobic digestion are that the process makes the treatment and disposal of large
           quantity of wastes such as poultry and dairy easier. Thus it helps to minimize prob-
           lem due to foul smell. The process helps to stabilize the waste and the fertilizer
           value of the original waste is retained with the digestion sludge.


           16.3.3 Adsorption process adsorbents in the elimination
                   of heavy metals

           The agroindustry waste can also be utilized as adsorbents in the elimination of
           heavy metals using the adsorption process. The presence of heavy metal ions
           (copper, cadmium, mercury, zinc, chromium, and lead ions) in higher concentra-
           tions than threshold can cause severe threats to many life forms. As compared to
           organic pollutants (i.e., susceptible to biodegradation) the heavy metal ions do not
           degrade into harmless end products. Many studies (Garg et al., 2004; Ngah and
           Hanafiah, 2008; Mo et al., 2018) have demonstrated the efficiency of adsorption
           process for the removal of heavy metal from waste using activated carbon. Many
           studies (Mondal et al., 2011; Low et al., 2011) have demonstrated the use of
           agroindustry wastes as a low-cost technique for the removal of heavy metals
           through the adsorption process. Various agroindustry wastes have been utilized,
           such as rice husk (Ayub et al., 2002), coconut husk (Tan et al., 1993), sawdust
           (Ajmal et al., 1996), sugarcane bagasse (Mohan and Singh, 2002), oil palm shell
           (Khan et al., 2003), neem bark (Ayub et al., 2002), etc., for the removal of heavy
           metals from wastewater.
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