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
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Hyperaccumulators
Some plants have demonstrated
a remarkable ability to accumulate several hundred times more metal
in shoot tissue than most plants. Hyperaccumulation involves translocating
metals from soil to shoot tissue in excess of 100 mg Kg-1 Cd, 1000 mg Kg-1
Ni or 10,000 mg Kg-1 Zn (Baker and Brooks, 1989). Unfortunately, hyperaccumulation
is often linked with slow growth rate and low biomass production, such
that net removal of metal contaminants via phytoextraction may not exceed
that of normal accumulators that produce large biomass.
The hyperaccumulation feature
of some plants is curious. Why would a plant have a mechanism to uptake
extremely high levels of metals for which there is no biological function?
Suggested explanations of hyperaccumulation include protection from predators
and pathogens, an effective method of tolerating high soil-metal concentrations
and a by-product of an aqcuisition mechanism designed to scavenge limited
nutrients (Kramer, 2000).
One of the most promising Cd hyperaccumulators is Thlaspi caerulescens,
a small forbe found in several parts of Europe. Many have been found growing
on heavily contaminated soils near smelters. Different strains have been
found and studied which apparently have different hyperaccumulating "specialties".
Different species of Thlaspi have been found to hyperaccumulate
Zn, Ni, Pb and Cd (Baker and Brooks, 1989). Baker (1994) found Cd accumulation
in a population of T. caerulescens from Whitesike, Britain of 164mg
Kg-1. Brown, et al. (1995) reported Cd accumulation in leaves of 29 mg
Kg-1 from a population at Prayon, Belgium. Lombi, et al. (1999) examined
a population of T. carulescens from the Cevennes region in southern France
and found Cd accumulation in shoots at a level much higher than the Prayon
or Whitesike populations at 500 mg Kg-1 (50% extraction of available Cd
in soil). It should be noted that all of these experiments were carried
out under different conditions, and are not directly comparable. Nevertheless,
Lombi, et al. (1999) did directly compare the three populations and found
the French population to be a superior hyperccumulator of Cd.
A drawback to the use of T.
caerulescens is that it has a rosette growth form and produces very
little biomass. The importance of its discovery lies more in understanding
the hyperaccumulation mechanism with an eye towards genetically manipulating
other plants to do the same.
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