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16 Bioreactors for the Production of Industrial Chemicals and Bioenergy Recovery from Waste
has to be done to balance the oxidation–reduction state, consequently in a lower
yield of biohydrogen [13]:
C6H12O6 + NAD+ →2CH3COCOOH + 2NADH + 2H+
(16.1)
Two directions can be established to outline molecular hydrogen production in
the presence of appropriate co-enzymes, for example, either by the re-oxidation of
NADH path or by formic acid disintegration pathway which could be represented
by Eqs. (16.2) and (16.3):
NADH + H+ + 2Fd2+ →2H+ + NAD+ + 2Fd+
(16.2)
2Fd+ + 2H+ →2Fd2+ + H2
(16.3)
16.3
Overview of Anaerobic Membrane Bioreactors
AnMBR technology is an excellent technology to control pollution because of its
lesser carbon foot print, while generating higher effluent (permeate) qualities
than conventional treatment practices. It is a combined method where membrane
element is attached with an anaerobic bioreactor [13, 17]. Membranes can remove
liquid from biomass and can preserve biomass efficiently in the bioreactor, thus
allowing the long SRT necessary for effective treatment, while permitting action at
the short HRT required for cost-effectiveness. It also gives possible benefits for the
bioprocesses where product formation and separation are required concurrently in
a compressed method [17]. Despite the applications, AnMBR configurations can be
characterized as submerged/immersed and exterior/side stream (Figure 16.3a,b). In
the previous case, membranes are immersed in the liquid state of biological reactor
or sometime submerged in a different reactor. In side stream structure, liquid
filtration membrane is connected to the bioreactor externally in a different unit
requiring a transitional pump step. Every design has positive and negative features
and, the attainable value of tetra-methyl pyrazine (TMP) is unlike and route of flow
is reverted. Higher TMP in side stream plan directed to diminish the substitute
area required for a particular filter through flux and enhance the claim of operation
energy. On the contrary, the maintenance and changing of membranes is effortless
in this configuration. Even though, submerged AnMBRs are less energy-intensive,
but well-established membrane surface area is requisite to deal with high permeate
fluxes [13, 16].
16.3.1
Challenges and Opportunities
16.3.1.1
Membrane Fouling and Energy Demands
Due to deposition of foulant materials, membrane fouling arise on the outside of
membrane and/or inside pore matrix which is a challenge within AnMBRs because
it worsens membrane permeability, thus demanding chemical cleaning which can
curtail membrane life time [17, 18]. A range of diverse foulants like particulates,
organics, colloids, microbes, and microbial byproducts, inorganics, and amalgama-
tion with thereof will cause fouling. Fouling naturally influences the economy of