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Bioremediation for Sustainable Environmental Cleanup
positive and gram-negative microorganisms (Barton et al. 2015). To improve culture resistance a
mixture of species is often selected for bioprecipitation processes (Kiran et al. 2017).
In addition to BSR, SRB have also been found to reduce other metal(loid)s with direct or
indirect microorganism activity. SRB can directly reduce metal(loid)s (i.e., Cr, As, Al, Te and Sb)
to a less toxic, insoluble form or can indirectly reduce metal(loid)s via hydrogen sulfide produced
during BSR (Sánchez-Andrea et al. 2016, Willis and Donati 2017). After metal(loid) reduction,
many species are capable of precipitation. For example, uranium (U6+) can precipitate uraninite
(UO2), chromium (Cr6+) in the presence of ferric iron (Fe3+) can precipitate chromium hydroxide
oxide (CrO (OH)) and chromium sulfide (Cr2S3) and arsenic can precipitate arsenic sulfide (As2S3)
and arsenopyrite (FeAsS). Metal(loid) reduction using SRB activity is presented in Table 2.3. The
following electron donors were used as an energy source in some of the noted reactions: acetate
(CH3COOH), formate (CH2O2), lactate (C3H6O3) and pyruvate (C3H4O3).
Table 2.3. Reduction of Metal(loid)s with SRB (Adapted from/Barton et al. 2015, Lovley 1993, Sahinkaya et al. 2017).
Metal(loid)
Electron Acceptor
Formula
Iron
Fe3+
CH3 COO– + 8Fe3+ + 4H2O → 2HCO3
– + 8Fe2+ + 9H+
CO2 H – + 2Fe3+ + H2O → HCO3
– + 2Fe2+ + 2H +
C3O3H5
– + 4Fe3+ + 2H2O → CH3COO– + HCO3
– + 4Fe2+ + 5H +
C3O3H3
– + 2Fe3+ + 2H2O → CH3COO– + HCO3
– + 2Fe2+ + 3H+
Fe0
Fe0 + 2H+ → Fe2+ + H2
Manganese
Mn4+
MnO2 → MnCO3 *
2H2S + MnO2 → MnS + S0 + 2H2O
Mn6+
Mn6+ → Mn2+*
Uranium
U6+
CH3COO– + 4U6+ + 4H2O → 2HCO3
– + 4U4+ + 9H+
H2 + U6+ → 2H+ + U 4+
Selenium
SeO4
2–
4CH3COO– + 3SeO4
2– → 3Se0 + 8CO2 + 4H2O + 4H+
CH3COO– + H+ + 4SeO4
2– → 4SeO3
2– + 2CO2 + 2H2O
SeO3
2–
2H2S + SeO3
2– +2H+ → SeS2 + 3H2O
Chromium
Cr6+
2Cr6+ + 3HS – → 2S0 +2Cr3+ + 3H+
Mercury
Hg2+
Hg2+ → Hg0*
Cobalt
Co3+
Co3+ + H2S → CoS + 2H+
Palladium
Pd2+
Pd2+ → Pd0*
Nickel
Ni3+
Ni3+ → Ni2+*
Technetium
Tc7+
Tc7+ → Tc4+*
Tc7+ → Tc5+*
Vanadium
V5+
V5+ → V3+*
Molybdenum
Mo6+
Mo6+ → Mo4+*
Arsenic
Ar5+
3Ar2S3 + 3H2S → 2H2As3S6
– + 2H+
As5+ → As3+*
Gold
Au3+
Au3+ → Au0*
Au+
Au+ → Au0*
* Not a full formula. Showing the redox couple.
Electron donors provide a carbon and energy source for the reaction. The selection of
an appropriate electron donor is the ratio of Chemical Oxygen Demand (COD) and sulfate ion
concentration (SO4
2–), i.e., COD/SO4
2– is important. There is a correlation between the interaction
of SRB with carbon source and electron acceptor (Barbosa et al. 2014, Kiran et al. 2017). The COD
denotes oxygen content required to oxidize the organic material and the electron acceptor is SO4
2–
(Barbosa et al. 2014). However, COD is measured under aerobic conditions, and therefore does not