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Bioremediation for Sustainable Environmental Cleanup
from the contaminant type, the concentration of the contaminant should also be estimated prior
to the phytoremediation to prevent the toxicity effects on healthy plants. The non-aqueous phase
pollutants create adverse effects on plant growth. Pollutants with low bioavailability are difficult to
extract with phytoremediation process (EPA 2000).
5.3.2.2 Selection of Plant Species
It requires substantial information regarding the plant biological system before deciding its
suitability for phytoremediation of a given area. The root system of the plants significantly affects the
phytoremediation potential. Fibrous roots offer the advantage of greater surface area for adsorption
and hence extraction of the pollutant. On the other hand, tap roots possess central large roots
extending in the deeper soil layers, thus can extract the pollutant from the deeper layers (Schwab
1998). The desirable root depth for phytoremediation varies for different plants. Non-woody plant
roots have shown efficient removal with feet depth, whereas tree roots less than 10–20 feet are found
to be most effective (Gatliff 1994). The scrutiny of seed source and seed health is also imperative
before commencing the phytoremediation process. Seeds from local regions are preferred as these
adapt to the environmental conditions easily (EPA 2000).
5.3.2.3 Climatic Conditions and site Accessibility
Climatic conditions such as temperature, moisture, rainfall and sunlight influence seed germination
and plant growth to a major extent. Thus, as a suitable candidate for phytoremediation, the
adaptability of the plant under climatic variations must be considered (EPA 2000). Consideration of
accessibility to the site is imperative before the commencement of the process as the consumption
of these plants by livestock or general public may lead to severe health consequences. Thus, edible
plants are not usually preferred for remediation (Ghavzan and Trivedy 2005).
Conclusively, phytoremediation is an economic, sustainable and environment friendly process
for soil reclamation. Moreover, the process is catalyzed by natural solar driven pumps and their
associated metabolic processes. It is also environmentally benign as it reduces water losses by
reducing its evaporation, limits soil erosion and prevents run-off that occurs due to heavy rain or
flooding.
5.4 Future Perspectives
Undoubtedly, the phytoremediation technology has proved beneficial over the conventional methods
for soil reclamation. However, there exists a gap between the process and its practical application.
• The strategy has been applied in laboratory and greenhouse tests, but its application extensively
at field studies should be tested.
• Another major problem of the process is the effective extraction, the contaminant is located
shallow enough for the plant roots to reach it, which is not possible in case of each contaminant.
• Longer lifecycle duration of most plants to attain the maturity stage also limits the application
of this process. Nowadays plants with a short lifecycle are being scrutinized to overcome this
problem.
• Extremely high levels of contaminants pose adverse effects on the plants’ growth and may even
led to plant death. Thus, the process is effective only for lower concentrations of contaminant.
References
Abdel-Shafy, H. I. and M. S. Mansour. 2016. A review on polycyclic aromatic hydrocarbons: source, environmental
impact, effect on human health and remediation. Egypt. J. Pet. 25(1): 107–123.
Agarwal, T. 2009. Concentration level, pattern and toxic potential of PAHs in traffic soil of Delhi, India. J.
Hazard.
Mater. 171(1-3): 894–900.