6.6 Bioremediation Process Using Biological Mediators
89
microorganisms. Biodegradation involves various steps depending on the contam-
inant and each step was initiated by specific enzymes which present in bacterial
cells. Biodegradation of contaminants by either internal or external enzymes will
break at any phase if a suitable enzyme is absent. Lack of specific enzymes is one
of the reasons for the accumulation of byproducts of contaminants. Hence, specific
enzyme-bearing microorganisms are introduced into the soil and water to improve
the activity of biodegradation. Indigenous bacterial cultures are capable of metab-
olizing contaminants. Biodegradation can be through either aerobic or anaerobic
mechanisms [34]. Several pesticide-degrading genes were identified on the plasmids
of soil bacteria, which are known as catabolic plasmids. They are found in the species
of Flavobacterium, Pseudomonas, Rhodococcus, and Alcaligenes which can degrade
pesticide contaminants.
6.6.2
Fungal Remediation
Fungi produce a variety of extracellular enzymes and fungal species possess high
capacity to degrade pesticides. Branching and filamentous fungal growth will per-
mit for effective colonization and examination of contaminated soil. White-rot fungi
are filament-like creatures and propose advantages over bacteria as they are better
oxidizers. They are strong organisms and are mostly extra tolerant to high concen-
trations of polluting chemicals than bacteria. Additional fungi that can be used in
bioremediation are zygomycetes, e.g. mycorrhizal and mucoraceous fungi. Anaero-
bic aquatic fungi can also be used for bioremediation [26].
6.6.3
Phytoremediation
It is the method which uses the living plants and their allied microorganisms
for in situ elimination and degradation of contaminants present in soil, ground
water, and surface water. Plants can accumulate and metabolize organic pollutants
(phytodegradation) or stimulate rhizospheric microorganisms (phytostimulation).
Phytoremediation is a less cost-consuming, eco-friendly, and easier for the remedi-
ation of adulterated soil and water using plants. Plants used will have an exclusive
and careful uptake capability of roots, with the translocation, bioaccumulation,
and degradation of contaminant. Plant-dependent soil remediation systems are
biological, solar-driven, and capable of self-extending uptake network systems
which enhance the underground ecosystem for productive use. Plant possesses a
favorable microenvironment in the root zone that leads to contaminant degradation.
In the soil, plant-associated bacteria are endophytic (nonpathogenic) and rhizo-
spheric. Endophytic bacteria effortlessly occur in the interior tissues of plants which
promote plant growth and degrade soil contaminants. Rhizospheric bacteria have
a capacity to degrade various agrochemicals due to enhanced microbial activity.
Advancements in recombinant DNA technology have created transgenic plants that
exhibit better-quality tolerance and catabolic activity against contaminants present
in the soil [35].