26.6 Biotechnological Approaches for the Removal of ECs
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windrows. The windrow can be thoroughly mixed by turning with a commercially
available turning machine. Moisture, pH, temperature, and explosive concentration
are monitored. After the completion of the composting, the windrows would be
disassembled and the compost will be taken to the final disposal area.
26.6.4.6
Land Farming/Land Treatment
Land farming is a simple bioremediation technique in which EC containing waste
or soil will be spread over a prepared bed and periodically tilled until pollutants are
degraded. The goal is to stimulate indigenous biodegradative microorganisms and
to facilitate their aerobic degradation of ECs. This practice is limited to the treat-
ment of superficial 10–35 cm of soil. Since land farming has the potential to reduce
monitoring and maintenance costs, and clean-up liabilities, it has received much
attention as a disposal alternative. Spilled oil and wood-preserving wastes have been
bioremediated by land farming treatments.
26.6.4.7
Biopiling
Biopiles are hybrid of land farming and composting. Essentially, engineered cells
are constructed as aerated composted piles. Adding compost to contaminated soil
enhances the bioremediation. Compost enhances the oxidation of the aromatic con-
taminants of the soil into ketones and quinones, which will eventually disappear.
This method is used for the treatment of surface of EC like petroleum hydrocarbons.
It is a refined version of land farming that tends to control physical loss of the EC
by leaching and volatilization. Biopiles provide a good environment for indigenous
aerobic and anaerobic microorganisms [9].
26.6.5
Phytoremediation
Phytoremediation involves the use of plants and their associated microbes to
accumulate, detoxify, or stabilize EC. It is an environment-friendly and sustainable
means of remediating contaminated soil and water. It has been an important aspect
of constructed wetlands, which is used to detoxify large volumes of wastewater with
dilute concentrations of EC successfully, including petroleum, hydrocarbons, chlo-
rinated solvents, pesticides, explosives, heavy metals, and radio nuclides. The most
important requirement for this method is the use of fast-growing, high-biomass
plants those are capable of uptaking and accumulating large amounts of toxic
metals. Biotechnology makes it possible to isolate such microbes and enrich the soil
so as to enhance phytoremediation by respective plants. The scientific studies on
genetics, physiology, and biochemistry of plant tolerance to inorganic and organic
contaminants have dramatically increased which will be important for improving
the phytoremediation techniques. These techniques for restoring soil at specific
level in determined site will depend on the chemical nature and concentration of the
pollutant and also on the physicochemical and biological characteristics of the soil.
However, there are still some barriers for the adoption of phytoremediation which
will impair the successful application of this remediation technique. This technique
is subdivided into number of phytoprocesses depending on the characteristic used
by the plants to remediate a polluted site.