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Presented by : A.R.M Sharif Nawyaz
Monisha Alam
Sharmeen Moushumi
Outline
• Definition
• Methods
• Process Descriptions
• Advantages & Disadvantages
• Applicability
• Limitation
• Cost & Performance
• Case Study
• Conclusion & Recommendations
What is In-Situ Bioremediation?
In place, on site Remediation by Microorganisms
In-situ Bioremediation
Process of In-Situ Bioremediation
Contaminant
intake
Digestion &
Metabolism
Non-toxic end
products released
Non Toxic End Products- CO2 & H2O (Aerobic)
CH4 , SO4
2- etc. (Anaerobic)
In-Situ
Bioremediation
Intrinsic/Natural Attenuation
(no site manipulation)
Enhanced/
Engineered Bioremediation
(site & microbial manipulation)
Biostimulation Bioaugmentation
Bioventing Air Sparging
Phyto-
remediation
Land
Farming
Methods of In-Situ Bioremediation
Alteration or manipulation of environmental conditions to
enhance microbial growth & activity
Lack of proper condition to
survive & growth
Bio-stimulation
Addition of adequate nutrients
(N, P, S, Ca, Mg etc)
Biostimulation
Soil unsaturated zone mostly aerobic O2 required
•Modification of
Soil Vapor
Extraction (SVE)
•Low air flow rate
• O2 in soil air
above 2%
Bioventing process
Bioventing
Landfarming
• Tilling soil, adding fertilizer, surfactants etc.
Bioaugmentation
Advantages Disadvantages
•Easy & Low cost
•Combines with
other technologies
•Less Fugitive emission
•Public acceptance
•Requires long time
•Contaminant
mobility increases,
leaching ground
water
•Less certainty of
uniform treatment
•Complete destruction,
no residuals
Advantages & Disadvantages
Site Conditions
Factors affecting
Contaminant
properties
Required Data: Soil properties and contaminants’
physical & chemical properties
Applicability
• Microorganisms present in soil able to degrade the
contaminants
• Adequacy of Nutrients – sufficient N, P, S, Ca, Mg etc.
• pH- 6 to 8
• Temperature – optimum 20° C to 30°C
• Moisture Content – 40-60% of the field capacity
• Bioavailability of contaminants to microorganism
• Oxygen availability – for aerobic microorganisms
• Soil Permeability & Homogenity
• Organic fraction of soil
Favourable Site Conditions
Following properties of contaminants affect applicability:
• Biodegradability
• Source
• Distribution in soil
• Solubility & sorption coefficient
• Chemical reactivity
• Volatility
Contaminant Properties
•Polyaromatic Hydrocarbons (PAH)
• Semi Volatile Organic Compounds (SVOCs, TCE & PCE)
• BTEX (Benzene, Toluene, Ethylene, Xylenes)
• Petroleum Hydrocarbons (PHC) (Gasoline, diesel, fuel)
• Pesticides
• Organic Solvents
• Wood Preservatives
Treated Contaminants
PAH Biodegradation
Limited to following site conditions:
•Low temperature – slows down biodegradation
• Clay, highly layered, or heterogeneous soil- limiting
transfer of oxygen or other electron acceptor
Limited for contaminants:
•Highly chlorinated organics like PCB
•heavy metals
•inorganic salt
Biodegradation resistant, because-
•Toxic for microorganism
•Microbes prefer feeding on other substrate
•Lack of microbes’ genetic capability to use them as source
of Carbon & energy
Limitations
Operational Limitations:
•Capacity of bioventing wells decreases with time
•Profuse microbial growth-clog the injection wells
•Circulation of water-based solutions through soil
increases contaminant mobility and necessitate
treatment of underlying ground water
Limitations (cont’d..)
• Effective if cleanup achieved in a compatible time
frame
• Simultaneous treatment of soil & ground water
• High efficiency of bioventing combined with SVE.
• Remediation time: 1 to several years
• Higher MW compounds take longer to degrade
Performance
• Less expensive over ex-situ methods
 Cost depends on: Site condition & Contaminants
• Larger site: lower unit cost
 In-situ bioremediation cost/m3
 Enhanced bioremediation: $30 to $100
 Bioventing: $ 79 to $928
 Phyto-remediation: $147 to $2322
 Other process cost/m3
In-Situ - SVE: $405-$1275,
Solidification/Stabilization: $150-$250
Ex-Situ - Biopiles: $130-$260
Composting: $370-$442
Cost
Site name &
Location
Contaminants Cost Duration
Reduction in
Contaminant
Concentration
Toronto,
Canada
BTEX, TPH
Approx.
$42/m3
Approx. 4
months (1995)
7,000 ppm to
<100 ppm
Longwood TS,
ON, Canada
BTEX, TPH
Approx. Total
$65,000
Approx. 30
days (1995)
14,000 ppm to
<100 ppm
Ontario,
Canada
PAH, PCP
Approx. Total
$741,000
1993-1994
439 mg/Kg to
10-50 mg/kg
Cost & Performance - Overview
CCME report 2001 estimated that 60% of
Canada’s contaminated sites involve PHC
contamination
Challenges faced
•Low temperature
•Characterization of contaminants
•Inappropriate analytical methods
•Complexity of site conditions
Application in Alberta
Site Strachan Gas plant – Near Rocky mountain House
Period Late summer to mid winter, 1994
Technology Bioventing preceded by SVE.
Contaminants NG gas condensate, BTEX, PAH, amine, BTEX Conc. 10-20
mg/L in HC plume.
Contaminant area- 1 hectre
Waste source LPG recovery area of the plant
Result Total removal 17,000 kg, 3,500 kg degraded through
Bioventing
Cost Capital cost: $150,000, Semiannual operating cost: $ 15,000
, unit cost about $10/kg
Details From Dec 1994 to march 1995 biodegradation rate: 200
kg/day, Air flow rate: 50 L/s
Case Study
Present condition of the site
Source : http://sulvaris.com/company/projects/
Conclusion & Recommendation
• Effective application in Canada & Alberta
• Bioventing preceded by SVE - better performance
• Inadequate site characterization-leads to under design or
overdesign; influence time!
• Low cost, lower risk to site workers & public
• Complete contaminant destruction
• Ecologically acceptable
In-Situ Bioremediation for Contaminated Soil

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In-Situ Bioremediation for Contaminated Soil

  • 1. Presented by : A.R.M Sharif Nawyaz Monisha Alam Sharmeen Moushumi
  • 2. Outline • Definition • Methods • Process Descriptions • Advantages & Disadvantages • Applicability • Limitation • Cost & Performance • Case Study • Conclusion & Recommendations
  • 3. What is In-Situ Bioremediation? In place, on site Remediation by Microorganisms In-situ Bioremediation
  • 4. Process of In-Situ Bioremediation Contaminant intake Digestion & Metabolism Non-toxic end products released Non Toxic End Products- CO2 & H2O (Aerobic) CH4 , SO4 2- etc. (Anaerobic)
  • 5. In-Situ Bioremediation Intrinsic/Natural Attenuation (no site manipulation) Enhanced/ Engineered Bioremediation (site & microbial manipulation) Biostimulation Bioaugmentation Bioventing Air Sparging Phyto- remediation Land Farming Methods of In-Situ Bioremediation
  • 6. Alteration or manipulation of environmental conditions to enhance microbial growth & activity Lack of proper condition to survive & growth Bio-stimulation Addition of adequate nutrients (N, P, S, Ca, Mg etc) Biostimulation
  • 7. Soil unsaturated zone mostly aerobic O2 required •Modification of Soil Vapor Extraction (SVE) •Low air flow rate • O2 in soil air above 2% Bioventing process Bioventing
  • 8. Landfarming • Tilling soil, adding fertilizer, surfactants etc.
  • 10. Advantages Disadvantages •Easy & Low cost •Combines with other technologies •Less Fugitive emission •Public acceptance •Requires long time •Contaminant mobility increases, leaching ground water •Less certainty of uniform treatment •Complete destruction, no residuals Advantages & Disadvantages
  • 11. Site Conditions Factors affecting Contaminant properties Required Data: Soil properties and contaminants’ physical & chemical properties Applicability
  • 12. • Microorganisms present in soil able to degrade the contaminants • Adequacy of Nutrients – sufficient N, P, S, Ca, Mg etc. • pH- 6 to 8 • Temperature – optimum 20° C to 30°C • Moisture Content – 40-60% of the field capacity • Bioavailability of contaminants to microorganism • Oxygen availability – for aerobic microorganisms • Soil Permeability & Homogenity • Organic fraction of soil Favourable Site Conditions
  • 13. Following properties of contaminants affect applicability: • Biodegradability • Source • Distribution in soil • Solubility & sorption coefficient • Chemical reactivity • Volatility Contaminant Properties
  • 14. •Polyaromatic Hydrocarbons (PAH) • Semi Volatile Organic Compounds (SVOCs, TCE & PCE) • BTEX (Benzene, Toluene, Ethylene, Xylenes) • Petroleum Hydrocarbons (PHC) (Gasoline, diesel, fuel) • Pesticides • Organic Solvents • Wood Preservatives Treated Contaminants
  • 16. Limited to following site conditions: •Low temperature – slows down biodegradation • Clay, highly layered, or heterogeneous soil- limiting transfer of oxygen or other electron acceptor Limited for contaminants: •Highly chlorinated organics like PCB •heavy metals •inorganic salt Biodegradation resistant, because- •Toxic for microorganism •Microbes prefer feeding on other substrate •Lack of microbes’ genetic capability to use them as source of Carbon & energy Limitations
  • 17. Operational Limitations: •Capacity of bioventing wells decreases with time •Profuse microbial growth-clog the injection wells •Circulation of water-based solutions through soil increases contaminant mobility and necessitate treatment of underlying ground water Limitations (cont’d..)
  • 18. • Effective if cleanup achieved in a compatible time frame • Simultaneous treatment of soil & ground water • High efficiency of bioventing combined with SVE. • Remediation time: 1 to several years • Higher MW compounds take longer to degrade Performance
  • 19. • Less expensive over ex-situ methods  Cost depends on: Site condition & Contaminants • Larger site: lower unit cost  In-situ bioremediation cost/m3  Enhanced bioremediation: $30 to $100  Bioventing: $ 79 to $928  Phyto-remediation: $147 to $2322  Other process cost/m3 In-Situ - SVE: $405-$1275, Solidification/Stabilization: $150-$250 Ex-Situ - Biopiles: $130-$260 Composting: $370-$442 Cost
  • 20. Site name & Location Contaminants Cost Duration Reduction in Contaminant Concentration Toronto, Canada BTEX, TPH Approx. $42/m3 Approx. 4 months (1995) 7,000 ppm to <100 ppm Longwood TS, ON, Canada BTEX, TPH Approx. Total $65,000 Approx. 30 days (1995) 14,000 ppm to <100 ppm Ontario, Canada PAH, PCP Approx. Total $741,000 1993-1994 439 mg/Kg to 10-50 mg/kg Cost & Performance - Overview
  • 21. CCME report 2001 estimated that 60% of Canada’s contaminated sites involve PHC contamination Challenges faced •Low temperature •Characterization of contaminants •Inappropriate analytical methods •Complexity of site conditions Application in Alberta
  • 22. Site Strachan Gas plant – Near Rocky mountain House Period Late summer to mid winter, 1994 Technology Bioventing preceded by SVE. Contaminants NG gas condensate, BTEX, PAH, amine, BTEX Conc. 10-20 mg/L in HC plume. Contaminant area- 1 hectre Waste source LPG recovery area of the plant Result Total removal 17,000 kg, 3,500 kg degraded through Bioventing Cost Capital cost: $150,000, Semiannual operating cost: $ 15,000 , unit cost about $10/kg Details From Dec 1994 to march 1995 biodegradation rate: 200 kg/day, Air flow rate: 50 L/s Case Study
  • 23. Present condition of the site Source : http://sulvaris.com/company/projects/
  • 24. Conclusion & Recommendation • Effective application in Canada & Alberta • Bioventing preceded by SVE - better performance • Inadequate site characterization-leads to under design or overdesign; influence time! • Low cost, lower risk to site workers & public • Complete contaminant destruction • Ecologically acceptable

Hinweis der Redaktion

  1. Sandy soil ,ornic fraction high or low,tunelling/channlling while adding nutrition due to homegeneoutty
  2. PAH as toxic but the end product was nontoxic and ,its kind of modified biodegradation
  3. PBs are calitrant