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          decolorize during reduction (Mu et al., 2009a). Biohazardous toxic com-
          pounds such as endocrine-disrupting estrogens can also be considered as medi-
          ator molecules in the MFC (Kiran Kumar et al., 2012). A few reports are
          available regarding the cathodic function in the effective removal of
          pollutants. Azo dyes (Mu et al., 2009a), nitrobenzene (Mu et al., 2009b),
          and nitrate (Lefebvre et al., 2008) are some of the pollutants studied in the
          cathode chamber of the BET. Hypothetically, it can be assumed that in the
          cathode chamber under anaerobic conditions most of the pollutants act as
          TEAs for power generation. Pollutants in the anodic chamber also act as medi-
          ators for electron transfer to the anode, which can increase the power gener-
          ation efficiency with a simultaneous reduction of pollutants, but very little
          work has been reported in the use of pollutants as mediators. Apart from sub-
          strate removal, considerable reduction of toxicity, color, and TDS in waste-
          water was also observed (Mohanakrishna et al., 2010a; Velvizhi and Venkata
          Mohan, 2011). The application of an MFC was also extended to treat solid
          waste and toxic aromatic hydrocarbons, taking advantage of the in situ biopo-
          tential and by considering the anode as the electron acceptor (Venkata Mohan
          and Chandrasekhar, 2011a,b). Studies related to the mechanisms of pollutant
          reduction and their role in electron transfer or acceptance will give a spectrum
          of practical feasibility of this technology for the removal of toxic pollutants.


          6.4.3 Electrically Driven Biohydrogenesis

          MEC is one of the recent advancements and a promising technology for the
          production of renewable and sustainable hydrogen gas. Use of the MEC
          provides a completely new approach for hydrogen generation from a wide
          variety of biomass, such as biowaste and wastewater and accomplishing
          waste treatment at the same time (Call and Logan, 2008; Cheng and Logan,
          2007; Ditzig et al., 2007; Liu et al., 2005; Logan, 2008; Rozendal et al.,
          2006, 2007). The principle of MEC is similar to the water electrolysis pro-
          cess, except that microbes (biocatalyst) are used in the anodic reaction to
                                                                         +

          degrade organic matter into CO 2 , electrons (e ), and protons (H )
                                  +

          (Figure 6.4). The e and H travel through the external circuit and mem-
          brane and are reduced to H 2 at the cathode. MEC operation is similar to the
          existing MFC operation except that the cathode is sealed in the anolyte in
          order to avoid oxygen, and an additional voltage is added to the circuit
          (Venkata Mohan et al., 2013c). An external potential is required because
                                                                          +
          under standard conditions, H 2 formation is not spontaneous. The H
          migrate to the cathode and get reduced to form H 2 in presence of e coming
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