1. VIVEKANADHA ARTS AND SCIEINCE
COLLEGE FOR WOMEN
Veerachipalayam,Sankagiri,Salem.
DEPARTMENT OF MICROBIOLOGY
TOPIC : PHYTOVOLATILIZATION
Guided By: Presented By:
Dr.R.Dinesh Kumar,. Bhuvaneswari.P
Assistant professor, I- Msc.Microbiology.
Department of microbiology.
SUBJECT :
BIOREMEDIATION
3. DEFINITION
Involves plants taking up contaminants them into volatile
forms and transpiring them into atmosphere.
Works on organic compounds and heavy metal
Contaminants ,TCE as well.
Mercury is the primary metal Contaminant that this process has Been
used for.
4. INTRODUCTION
Phytovolatilization involves the uptake of
Contaminants by plant roots and its conversion
to a gaseous state, and release into atmosphere.
This process is derived by the evaopotion spiration of plants.
Plants that have high evaopotran spiration rate
sought after in phytovolatilization.
Organic contaminants ,especially volatile organic compounds are
passively
Volatilized by plants.
FOR EXAMPLE;
Hybrid poplar trees have been used to volatilize trichloroethylene by
converting it to chlorinated acetates and CO2.
5. TYPES
Two different types of phytovolatilization.
Such as,
(A) Direct phytovolatilization,
(B) Indirect phytovolatilization.
6. Direct Phytovolatilization
Direct phytovolatilization is the more intuitive
and better studied form, resulting from plant
Uptake and translocation of contaminants.
It leads to volatilization of the compound from
The stem/trunk and leaves.historically this
Process is simply called phytovolatilization.
The direct phytovolatilization pathway often
Differs from transpiration.
7. INDIRECT PHYTOVOLATILIZATION
Indirect phytovolatilization is the increase in Volatile
contaminant flux from the subsurface
resulting from plant root activities.these process
Cause profound changes in subsurface chemical
Fate and transport.
The activites of plant roots can increase the
Flux of volatile contaminants from the
Subsurface through the following mechanism;
Lowering the water table.
Increased soil permeability.
Chemical transport via hydraulic redistribution.
10. ADVANTAGES
Contaminants removal from soil.
Transformed to less toxic products.
No residuals management.
The contaminant,mercuricion, may be transformed into less toxic
substance.
11. DISADVANTAGES
Moving problem from one media to another.
Possible air monitoring.
The mercury released into the atmosphere is
likely to be recycled by precipitation and then
Re-deposited back into lakes and oceans,
repeating the production of methyl-mercury by
anaerobic bacteria.