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Rhizofiltration

Rhizofiltration involves absorption, precipitation and accumulation of metals in roots only, there being no involvement of shoots. A plant should have rapidly growing roots to be able to remove toxic metals from water and soil for an extended period of time.

Bioaccumulation coefficients of roots of most plants are also known to be relatively much higher than those for shoots. Rhizofiltration provides a cheap method of clean-up for low concentration of contaminants in large volumes of water, so that for radionuclide contaminated waters, it may be particularly suitable, more so when used in combination with micro-organism based bioremediation strategy.

A number of plant species including rapeseed mustard (B. juncea), rye, corn and sunflower can have rapidly growing roots and can be used for rhizofiltration. Different metals are removed by roots, perhaps utilizing different mechanisms. For instance, in case of Pb, passive surface absorption (e.g. chelation, ion exchange and specific adsorption) by the roots (living or dead) is the fastest method of metal removal. Other biological processes including intracellular uptake, vacuolar deposition, and translocation to the shoot are relatively slower. Root mediated precipitation of Pb in the form of Pb phosphate is the slowest process. Cell walls of roots can also accumulate Pb in the form of PbCO3 formed due to respiratory CO2.

Shoot and root bioaccumulation coefficients of B. juncea and T. caerulescens (bioacc. coeff. = metal conc. in plant/metal conc. in solution mg/g DW)

Toxic metal

Shoot

Root

 

Brassica

Thlaspi

Brassica

Thlaspt

Cd(5)

175

50

20574

4258

Cu(1)

159

623

55809

60716

Cr(0.4)

080

89

5486

8545

Ni(1)

587

2739

11475

8425

Pb(5)

003

29

1432

7011

Zn(3)

049

770

1816

2990