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

pH

     pH refers to the concentration of hydrogen ions (H+) in a substrate such as soil. pH is measured on a logarithmic scale such that each numerical increase in pH corresponds to a decrease in H+ by a factor of ten. A pH of 1 is considered acidic because it has a very high H+ concentration and a pH of 13 is considered very alkaline because it has almost no free H+. pH dramatically effects the CEC of soil by limiting the available exchange sites at low pH. H+ bind to soil particles tighter than other cations, thus, any metal bound to a soil particle will get booted off in the presence of excess H+ (Garcia-Miragaya and Page, 1978). At low pH (<6), H+ is in excess and replaces all other cations on the micelle, thus making them bioavailable. At high pH (>7), cations are less bioavailable because they have less competition from H+ for available binding sites. Many cations bind to free hydroxyl groups (OH-) and form insoluble hydrous metal oxides which are unavailable for uptake, such as CdCO3 (Salisbury and Ross, 1992; Ramachandran, 1999). Evergreens in alkaline soils turn yellow due to lack of available iron (Fe), similarly, many plants experience aluminum (Al) toxicity in low pH soils. 
 
     Decreasing the pH of soil will increase Cd bioavailability, and will usually increase plant uptake of Cd unless the Cd elicits a toxic response in the plant. Optimum Cd mobility is achieved at pH = 4.5 - 5.5 (Bingham, 1980). Therefore, altering soil pH by adding an acid is a viable method for increasing Cd bioavailability, a strategy already utilized by many plants that release organic acids for nutrient scavenging (Salisbury and Ross, 1992).
 


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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