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Phytoremediation of Toxic Organics Direct: Plant may release enzyme to the environment that break down the organic contaminants which result in detoxification Indirect: Plant provide a favorable environment in the rhizosphere for microbial growth that result in break down of soil contaminants. Plant release organic acids or

Phytoremediation of Toxic Organics Direct:

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Phytoremediation of Toxic Organics Direct: Plant may release enzyme to the environment that break down the organic contaminants which result in detoxification Indirect: Plant provide a favorable environment in the rhizosphere for microbial growth that result in break down of soil contaminants. - PowerPoint PPT Presentation

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Page 1: Phytoremediation of Toxic Organics Direct:

Phytoremediation of Toxic Organics

Direct:• Plant may release enzyme to the environment that

break down the organic contaminants which result in detoxification

Indirect:• Plant provide a favorable environment in the

rhizosphere for microbial growth that result in break down of soil contaminants.

• Plant release organic acids or chelating agents that increase solubility of the contaminant, which result in increased degradation by soil microorganisms.

Page 2: Phytoremediation of Toxic Organics Direct:

Plant derived degradative enzyme:

Five plant derived enzymes have been identified that can degrade soil contaminants, including nitrate and nitrite reductase, laccase, nitrilase, and dehalogenase.

(Note: over 50 soil enzymes have been detected. Presumably, they are mostly microbial origin.)

Page 3: Phytoremediation of Toxic Organics Direct:

• Nitrate reductase: involved in reducing nitrate to nitrite

• Nitrite reductase: involved in reducing nitrite to ammonium

• Nitrilase: also named nitrile aminohydrolase. Acts on a wide range of aromatic nitriles and some aliphatic nitriles. (CN)

• Laccase: A group of multi-copper proteins of low specificity acting on both o- and p-quinols, and often acting on aminophenols and phenylenediamine and produce semiquinone.

• Dehalogenase: degrades hexachloroethane (Cl3C-CCl3) and TCE (ClHC=CCl2).

Page 4: Phytoremediation of Toxic Organics Direct:

Example: Filed trials of phytoremediation of petroleum-contaminated soils by researchers at Kansas State Univ.

Objectives:

1. To evaluate effect of plant species2. To determine the effect of management

techniques3. To develop protocols for quantification of

contaminants in large numbers of soils.

Page 5: Phytoremediation of Toxic Organics Direct:

Three field trials were chosen:

1. CRO. Crude oil site locate near the Gulf of Mexico

2. CAR. California refinery site3. VAD. Virginia diesel contaminated site

Page 6: Phytoremediation of Toxic Organics Direct:

Schwab and Banks, 1999

Page 7: Phytoremediation of Toxic Organics Direct:

Schwab and Banks, 1999

Page 8: Phytoremediation of Toxic Organics Direct:

Schwab and Banks, 1999

Page 9: Phytoremediation of Toxic Organics Direct:

Schwab and Banks, 1999

Page 10: Phytoremediation of Toxic Organics Direct:

• CRO site has been returned to its original agricultural use and the others are still being treated.

• At least two growing season is required to return the site for agricultural use.

Page 11: Phytoremediation of Toxic Organics Direct:

Potential and limitations of phytoremediation

• Not competitive if a quick remediation is needed.

• Not appropriate if immediate risk of groundwater contamination exist due to imperfect containment of pollutants against leaching

• Limited by conditions that inherently limit plant growth.

• Suitable for remediation of large surface contaminated areas. Contaminated soil could be used to produce energy and fiber crops.

Page 12: Phytoremediation of Toxic Organics Direct:

Phytoremediation of TCE in Groundwater using Populus

Hybrid poplar (Populus charkowiiensis x incrassata, NE 308) at Edward Sears Property

Page 13: Phytoremediation of Toxic Organics Direct:

Air Force Plant 4 Phytoremediation Site Layout, Carswell Air Force Base - Ft. Worth, TX