2. Why environmental biotechnology?
It is needed to:
eliminate the hazardous wastes
produced by our other
technologies.
distinguish between similar
species and ensure species are not
at risk of extinction.
create alternative energy sources
(i.e. Biofuel).
3. Definitions
Bioremediation is any process that uses organisms
(microorganism, algae and plant) or their enzymes to return
the polluted environment to its original condition.
Biodegradation is the use of these organisms in the
degradation of different pollutants.
Xenobiotic compounds are chemical compounds found in an
organism but it are not normally produced or expected to be
present in it.
Cometabolism: in this process the microorganism produces
an enzyme to utilizes its nutrients, but by chance this enzyme
can degrade a pollutant.
4. Bioremediation is a triple-corners process:
Organisms
Pollutants
Environments
Microorganisms
Plants
Enzymes
Soil
Water
Air
Organic
Inorganic
Solid
Liquid
Gas
6. Stages of a biodegradation study
1- Isolation of the microorganism
5- Determination of the biodegradation
efficiency
4- Optimization of the biodegradation
conditions
3- Identification of the microbial isolate
2- Purification of the obtained isolates
6- Identification of the biodegradation products.
7- Cell or enzyme immobilization.
8- Enzyme identification.
7. Immobilized enzymes (or cells) is defined as the enzyme that
physically or chemically confined in defined materials with
retention of its catalytic activity.
Cells and Enzymes immobilization:
The immobilization
methods
1- Carrier-binding
methods.
2- Cross-linking
methods.
3- Entrapping methods.
1) Covalent binding methods
2- Ionic binding methods.
3- Physical adsorption.
4- Bio-specific binding methods.
3- Membrane.
2- Microcapsule.
1- lattice method.
4- Reversed micelle.
8. 1- Polysaccharides: cellulose, dextran and agarose
derivatives.
2- Proteins: gelatin, albumin.
3- Synthetic polymers: Polystyrene derivatives, ion
exchange resins, polyurethane.
4- Inorganic materials: glass, sand, ceramic and
magnetite.
Materials used in the Carrier-binding methods
9. 1) Covalent binding methods include:
a) Cyanogen Bromide method (CNBr).
b) Acid-azide derivative method
c) Condensing reagent methods
d) Diazo coupling methods
e) Alkylation methods.
Figure1: Steps of CNBr enzyme immobilization method
10. By cross-linking of the enzyme molecules by reacting with
glutaraldehyde.
A cross-link is a bond that links one polymer chain to another.
B- Cross-linking methods:
11. 3- Materials used in the entrapping methods
a) Lattice type:
polyacrylamide,
calcium algenate,
polyvinylalcohol polymers.
b) Microcapsule type:
Interfacial Polymerization Method.
Liquid drying method.
12.
13. Phytoremediation
Phytoremediation is use of plants for accumulation,
removal or conversion of pollutants.
Phytoremediation
Phytostabilization
Phytotransformation Phytoextraction
Phytovolatilization Phytostimulation
14.
15. Approximately 400 plant species have been classified as
hyperaccumulators of heavy metals, such as grasses,
sunflower, corn, hemp, flax, alfalfa, tobacco, willow, Indian
mustard, poplar, water hyacinth, etc.
16. The root exudates of these plants play an
important role in phytoremediation as it
activate the surrounded microorganisms.
Genetic engineering are used as in case of
BT protein or insect pheromones
producing plants to reduce the use of
pesticides.
20. The biosurfactants are chemical compounds
characterized by hydrophobic and hydrophilic (non-
polar and polar) regions in one molecule
(amphipathic molecules).
Biosurfactants from bacteria, cyanobacteria, fungi
and yeast are classified into:
1) Glycolipids.
2) Lipopeptides.
3) Phospholipids.
4) Glycoproteins.
5) Polymeric biosurfactants.
Biosurfactants
21. Glucolipid from Alcaligens sp.
Glucolipid from Alcalivorax sp.
Trehalose tetra ester from Arthrobacter sp.
Chemical structure of some biosurfactants
22. Physiological roles of biosurfactants:
1- Increase the availability of hydrophobic compounds
2- Nutrient storage molecules.
3- Save the microbial cells from toxic substances.
4- Efflux of harmful compounds.
5- Extracellular and intracellular interactions such as quorum
sensing and biofilm.
23. Biosurfactant applications in
bioremediation:
The microbe may access a poorly water-
soluble substrate that has been
“pseudosolubilized” by the biosurfactant.
Reduce the adsorption of the non-polar
pollutants to the surface of soil particles.
24. Bioremediation techniques:
(1) In-situ (without excavation).
(2) Ex-situ (with excavation).
Only ex-situ processes allow an efficient optimization of
incubation parameters (biostimulation), including:
pH,
Aeration,
Agitation,
Moistening
nutrients,
solvents or surfactants.
In addition to addition of microorganisms (bioaugmentation).
26. 1- High density poly ethylene (HDPE)
2- Sump pump to collect leachate
3- Layer of pea gravel
4- Layer of polluted soil to be treated
5- Chopped alfalfa hay to retain moisture
6- Wheels on sprinkler piping system
7- Piping frame, aluminum or PVC pipes with
frequent holes, sufficient to allow water,
nutrients and bacteria to treat the land farm
plot
8- Flexible leachate collection hose
9- Bypass valve that allows leachate to be
circulated directly to water distribution tank,
10- Recirculation hose
11- Alken-Murray Bioactivator 2000,
bioreactor unit
12- Fresh water supply hoses
13- Pumps for fresh water
14- Treated water hose
15- Water distribution tank
16- Pump for distribution tank
27. B- Water and gas bioremediation:
Biofiltration is a process, in which,
microorganisms supported on inert materials
are used to degrade organic pollutants for air,
gas and water bioremediation.
Types of biofilters:
1- Bioscrubbers.
2- Biotrickling filters.
3- Slow sand or carbon filters.
29. Slow sand or carbon filters
Slow sand or carbon filters work through the formation
of a gelatinous layer (or biofilm layer) on the top few
millimetres of the fine sand or carbon layer.
This layer contains bacteria, fungi, protozoa, rotifera
and a range of aquatic insect larvae (i.e. rotifers).