5.5 Bioremediation – The Emerging Sustainable Strategy
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Table 5.3
Adaptive mechanisms in microorganisms resulting in metal resistance
physiology.
Adaptations
Features
References
Extrusion system
Metals are pushed out through the cells using
mechanisms such as chromosomal or
plasmid-mediated events
[4]
Biotransformation
Microorganisms convert the toxic metal to
non-toxic forms
[6]
Degradation
enzymes
Using enzymes such as oxidases and reductases:
microbes produce these enzymes to convert
pollutants to metabolic products
[20]
Exopolysaccharides
(EPS)
Microorganisms get adapted to the contaminated
surrounding by secreting EPS, which develops as
an outer hydrophobic cell membrane comprising
efflux pumps against the cell membrane
disrupting contaminants (e.g. solvents)
[4, 21]
Metallothioneins
The metal-binding proteins to which metals form
a complex
[22]
Metal ions bind to the bacterial cell surface via different interactions such as cova-
lent bonding and electrostatic and van der Waals forces. Microorganisms that act as
metal accumulators possess an inherent property of converting toxic form of metal
contaminants to non-toxic or less toxic form. The life cycle of microorganisms are
intricately associated with the biochemical cycle of different heavy metals, which
also influences the process of redox transformations of environmental heavy metal
leading to different oxidation states with different solubility and mobility, therefore
influencing the toxicity factor.
Certain microorganisms in nature have evolved genetic machinery that encodes
cellular circuitry that orchestrates to ensure heavy metal resistance for the
metal-contaminated ecological niche (Table 5.3). Scientific studies have previously
reported myriad microorganisms having heavy metal remediation capabilities.
Efficient Ni removal was observed with Escherichia coli AS21 previously [23].
Arsenic remediation was observed in Micrococcus sp. isolated from the paddy field
of West Bengal, India [6]. Earlier studies have also reported Cd, Cr, Hg, and Pb
decontamination in a microbe-assisted way in Bacillus subtilis 38 (B38) [24].
An array of resistance strategies have been reported in microorganisms that could
resist high metal concentrations, for instance, extracellular sequestration, alteration
in cell morphology, altered permeability, precipitation of heavy metals, and biosorp-
tion of heavy metals [1]. Microbes could accumulate heavy metals within the cell
by utilizing different metabolic pathways that have been extensively studied and
observed in a wide range of microbes [6]. Both Gram-positive and Gram-negative
bacteria have some cellular components such as teichoic acid, polypeptide, and pro-
tein, such as metallothionein, which helps in cellular accumulation and conversion
to less toxic form. Earlier studies have reported that Pseudomonas aeruginosa was