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

 
Soil amendments

     Adding sand to the soil will decrease the overall cation exchange capacity since sand does not bind cations. The problem with this is that the CEC of the clay is still the same and since it is not being removed,  the net gain in availability of metals is small. 
 
     Organic matter is commonly added to soil to lower pH. This is seemingly a good way to increase Cd bioavailability, but could actually backfire since Cd binds to organic matter with high affinity (Street, 1977). Thus, addition of organic matter could actually decrease Cd bioavailability, despite the decrease in pH conferred.

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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