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

Phytoremediation

     Plants can extract Cd from the soil and transport it via the xylem into shoots and leaves where it can accumulate (Blaylock, et al. 1997) . It has been shown that pollutants can be removed from a contaminated site by harvesting the plant biomass containing the pollutant. This is referred to as phytoextraction (Chaney, 1983). Sometimes, plants will simply stabilize the contaminant in the soil through various mechanisms (phytostabilization), and this is also sometimes desirable (Kabata-Pendius and Pendius, 1992). Other aspects of phytoremediation focus on the ability of plants to directly or indirectly degrade pollutants (phytodegradation, phytostimulation, phytovolatilization) but since metals cannot be degraded the way organic molecules can, only phytoextraction and phytostabilization are applicable to Cd remediation. 
 


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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