BIOREMEDIATION
Presented by
KARTHIKA MOHANAN
 Bioremediation is a process in which microorganisms degrade
organic contaminants or immobile inorganic contaminants
 Also known - enhanced bioremediation or Engineered
bioremediation
 Bioremediation is commonly used for the treatment of soils
contaminated with organic compounds (petroleum hydro
carbons)
 -cannot degrade heavy metal but can change valance states
(hexavalent chromium to trivalent chromium)
 Based on microorganisum used:-
Aerobic, cometabolic, and anaerobic
 Based on location :-
In-situ bioremediation & ex-situ bioremediation
 Based on presents of microorganism:-
Indigenous microorganisms – Microorganisms are native to
site.
Exogenous microorganisms – Microorganisms are taken from
other locations, cultured in laboratory, then added to
contaminated soil
Requirements
 Condition for microorganisms to grow and survive
 pH - should be between 5.5-8.5
 Temperature - between 15-45oc
 Oxygen - >2mg/L aerobic reaction
- < 2mg/L anaerobic reaction
 Nutrients -carbon, hydrogen, oxygen, nitrogen, phosphorus
The actual quantity of these nutrients depends on
the BOD of contaminated soil.
 Toxicity - High conc. of contaminants can be toxic
Some contaminants even at low conc. may be toxic
Fundamental Process
Bioremediation processes may be directed toward
accomplishing:
1.Destruction of organic contaminants
2.Oxidation of organic chemicals thereby the organic
chemicals are broken down to smaller constituents
3.Dehalogenation of organic chemicals by cleaving chlorine
atoms or other halogens from a compound
Degradation is a complex oxidation - reduction reaction.
The electrons or reducing equivalents produced must be
transferred to a terminal electron acceptor (TEA)
Depending upon TEA, bacteria are grouped into three
categories:
 Aerobic bacteria – Only use molecular oxygen as a TEA
 Facultative Aerobes / Anaerobes – Which can utilize
oxygen or when oxygen is low or non-existent may
switch to nitrate, manganese oxides or iron oxides as TEA
 Anaerobes – They utilize sulfate or carbon dioxide
Advantages
Complete degradation of organic compounds to non-toxic by-
products
Minimum mechanical equipment requirements
Can be implemented as in-situ or ex-situ process
Cost is low
Disadvantages
 There is a potential for partial degradation to equally toxic,
more highly mobile by-products
 The process is highly sensitive to toxins and environmental
conditions
 Excessive monitoring required
 Difficult to control volatile organic compounds during an ex-
situ process
 A longer treatment time required
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BIOREMEDIATION new.ppt

  • 1.
  • 2.
     Bioremediation isa process in which microorganisms degrade organic contaminants or immobile inorganic contaminants  Also known - enhanced bioremediation or Engineered bioremediation  Bioremediation is commonly used for the treatment of soils contaminated with organic compounds (petroleum hydro carbons)  -cannot degrade heavy metal but can change valance states (hexavalent chromium to trivalent chromium)
  • 3.
     Based onmicroorganisum used:- Aerobic, cometabolic, and anaerobic  Based on location :- In-situ bioremediation & ex-situ bioremediation  Based on presents of microorganism:- Indigenous microorganisms – Microorganisms are native to site. Exogenous microorganisms – Microorganisms are taken from other locations, cultured in laboratory, then added to contaminated soil
  • 4.
    Requirements  Condition formicroorganisms to grow and survive  pH - should be between 5.5-8.5  Temperature - between 15-45oc  Oxygen - >2mg/L aerobic reaction - < 2mg/L anaerobic reaction  Nutrients -carbon, hydrogen, oxygen, nitrogen, phosphorus The actual quantity of these nutrients depends on the BOD of contaminated soil.  Toxicity - High conc. of contaminants can be toxic Some contaminants even at low conc. may be toxic
  • 5.
    Fundamental Process Bioremediation processesmay be directed toward accomplishing: 1.Destruction of organic contaminants 2.Oxidation of organic chemicals thereby the organic chemicals are broken down to smaller constituents 3.Dehalogenation of organic chemicals by cleaving chlorine atoms or other halogens from a compound
  • 6.
    Degradation is acomplex oxidation - reduction reaction. The electrons or reducing equivalents produced must be transferred to a terminal electron acceptor (TEA) Depending upon TEA, bacteria are grouped into three categories:  Aerobic bacteria – Only use molecular oxygen as a TEA  Facultative Aerobes / Anaerobes – Which can utilize oxygen or when oxygen is low or non-existent may switch to nitrate, manganese oxides or iron oxides as TEA  Anaerobes – They utilize sulfate or carbon dioxide
  • 7.
    Advantages Complete degradation oforganic compounds to non-toxic by- products Minimum mechanical equipment requirements Can be implemented as in-situ or ex-situ process Cost is low
  • 8.
    Disadvantages  There isa potential for partial degradation to equally toxic, more highly mobile by-products  The process is highly sensitive to toxins and environmental conditions  Excessive monitoring required  Difficult to control volatile organic compounds during an ex- situ process  A longer treatment time required
  • 9.