Mechanisms and Strategies for Phytoremediation of Cadmium

INTRODUCTION
    Phytoremediation
    Advantages of  Phytoremediation
    Limitations of Phytoremediation

BIOAVAILABILITY OF CADMIUM 
    Cation Exchange Capacity (CEC)
    pH
    Soil Amendments
    Competitive Cations
    Fertilizer
    Mycorrhizae
    Chelation
       Phytochelatins (PCs)
       Phytochelatin Effectiveness
       Role of Sulfur in PCs
       Oxidative Stress
       Translocation
       Metallothioneins
       Organic Acids
       EDTA / EGTA

CADMIUM TOLERANCE AND
ACCUMULATION IN PLANTS
    Cell Wall Binding
    Reduced Transport
    Compartmentalization
    Chelation
    Phytoextraction factors
       Table 1.  Plant Accumulation
       Hyperaccumulators

CONCLUSIONS

LINKS

BIBLIOGRAPHY

Advantages of Phtyoremediation

     Phytoremediation has received considerable attention because it offers a cheaper, easier and environmentally sound pollution-remediation option. Seeding a field of plants and harvesting them to extract the pollutant  is much cheaper than removing huge amounts of contaminated soil. In some cases, the extracted biomass can be incinerated and the metals recovered and sold for profit (Salt, et al. 1998). In cases where it is not economically feasible to recycle the metals, it is still cheaper to dispose of a small amount of contaminated plant mass in a hazardous waste landfill rather than acres of topsoil. Phytroremediation is non-invasive and does not require heavy machinery to excavate soil. For this reason it is aesthetically more pleasing. Most importantly, it is a real solution to cleaning up a substrate. Excavating and transferring contaminated soil or water to a hazardous waste storage facility is simply moving the problem without cleaning anything, whereas phytoredmediation is real remediation of the substrate.
 
 

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Page Created 4-18-00
Sam Cox
Department of Horticulture
Colorado State University
samcox@lamar.colostate.edu
http://lamar.colostate.edu/~samcox/index.htm