Page 199 - Soil Degradation, Conservation and Remediation
P. 199

188                                                   6 Soil Pollution

                 Landfarming : In this technique, contaminated soil is excavated and spread over a
              prepared bed and periodically tilled until pollutants are degraded. Indigenous
              biodegradative microorganisms are stimulated which facilitate their aerobic
              degradation of contaminants. The practice is limited to the treatment of superfi cial
              10–35 cm of soil.
                Composting : It involves combining contaminated soil with nonhazardous organic


              ammendments  such as manure or agricultural wastes.  The presence of these
              organic materials supports the development of a rich microbial population and
              elevated temperature characteristic of composting.
                Biopiles : Biopiles are a hybrid of landfarming and composting. Essentially,
              engineered cells are constructed as aerated composted piles. Typically used for
              treatment of surface contamination with petroleum hydrocarbons, they are a refi ned
              version of landfarming that tend to control physical losses of the contaminants
              by leaching and volatilization. Biopiles provide a favorable environment for
              indigenous aerobic and anaerobic microorganisms (von Fahnestock et al.  1998 ).
                Bioreactors : Slurry reactors or aqueous reactors are used for ex situ treatment of
              contaminated soil and water pumped up from a contaminated plume. It involves
              the processing of contaminated soil through an engineered containment system.



               Phytoremediation

             The use of plants for in situ treatment of pollutants in soils, sediments, and water is
            known as phytoremediation. Phytoremediation is a relatively new technology that
            offers clear advantages over traditional methods for site cleanup. Some of its
            applications have only been assayed at the laboratory or greenhouse level, but
            others have been field tested sufficiently to allow full-scale operational (Campos


            et al.  2008 ). It is best applied at sites with relatively shallow contamination of
            pollutants that are amenable to phytoextraction, phytovolatilization, phytodegradation,
            and/or phytostimulation.
                 Phytoextraction : the uptake of contaminants in plant roots and their concentration
              in harvestable tissues
                Phytovolatilization : the uptake of contaminants by plants and their subsequent
              release into the atmosphere in a volatile form
                Phytodegradation : biodegradation of pollutants by plant enzymes
                Phytostimulation : biodegradation of pollutants by plants, facilitated by microorganisms
              in the rhizosphere

                This technology is especially valuable where the contaminated soils are fragile and
            prone to erosion. Phytotransformation and rhizosphere bioremediation are applicable
            to sites contaminated with organic pollutants that include pesticides. It is cost-effective
            and has aesthetic advantages and long-term applicability (Brown  1995 ). Plants can
            withstand relatively high concentrations of organic chemicals without toxic
            effects, and they can uptake and convert chemicals quickly to less toxic metabolites
            in some cases. In addition, they stimulate the degradation of organic chemicals in the
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