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Bioremediation

  1. BIOREMEDIATION 1
  2. INTRODUCTION • Bioremediation is defined as the use of biological treatment systems to destroy or reduce the concentration of hazardous wastes from contaminated sites. • Economical, safety • Cost-effective, permanent solution to clean up soils contaminated with xenobiotic compounds • At least six times cheaper than incineration and three times cheaper than confinement 2
  3. Introduction • New and exciting field • Performed off-site when contamination is superficial, but it will have to be in situ when the contaminants have reached the saturated zone • General components and characteristics Microbial systems Type of contaminant Geological and chemical conditions at the contaminated site 3
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  5. Advantages • Can be done on site • Minimum site disruption is caused • Eliminates transportation costs and liabilities • Eliminates long-term liabilities • Uses biological system, often less expensive • Can be coupled with other treatment techniques 5
  6. Disadvantages • Some chemical compounds are not biodegradable • Extensive monitoring required • Each site has specific requirements • Potential production of toxic unknown sub-products is possible • Strong scientific support is needed 6
  7. BIOREMEDIATION TECHNIQUES 7
  8. Bioremediation techniques • Divided into 3 categories : In-situ, ex-situ and ex-situ slurry • In situ - soil and associated ground water is treated in place without excavation • Ex situ – excavated prior to treatment • Ex situ slurry – creation and maintenance of soil- water slurry as bioremediation medium • Slurry can be maintained either in a bioreactor or in a pond lagoon 8
  9. In situ remediation techniques 9
  10. In situ remediation techniques • Bioremediation on land • Land farming • Bioventing • Biosparging • Bioaugmentation 10
  11. Bioremediation on land • Depend on the area contaminated, the properties of the compounds involved, the conc of contaminants, time required to complete the bioremediation • The contamination can be treated on site or the contaminated material excavated and treated on or off site. • If contaminant is water soluble a pump-and-treat technique used • Introduced into contaminated areas and removed at another site to be treated on or off site 11
  12. Land farming • The simplest of the on-site treatment • Involve mixing of the soil by ploughing or some form of mechanical tilling • Ploughing increases the O₂ levels in the soil and distributes contaminants more evenly, which increases the rate of degradation. • Nutrients added to increase biodegradation • 4-6 months required to remove contaminants such as PAHs 12
  13. Land farming • Method is best suited for shallow contamination of soil surface • Treatment area is lined and dammed to retain any contaminated leachate • Rate of degradation depends on the microbial pollution, the type and level of contamination, and the soil type • Avg half-life for the degeneration of diesel fuel and heavy oils is in the order of 54 days with this type of system 13
  14. Land farming 14
  15. Bioventing • In situ process, which combines an increased oxygen supply with vapour extraction • A vacuum is applied at some depth in the contaminated soil • This draws air down into the soil from holes drilled around the site and sweeps out any volatile organic compounds • Nutrient supplementation can be provided by running nutrients into trenches dug across the site 15
  16. Bioventing • The increased supply of air will increase the rate of natural degradation by the aerobic micro-organisms. • Only effective for reasonably volatile compounds, where soil is permeable • Vapour extracted may need some form of treatment • One biological solution is the use of biofilters 16
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  18. Biosparging • Process to increase the biological activity of the soil by increasing the supply of oxygen by sparging air or oxygen into the soil • Air injection replaced by pure oxygen – increase degradation rates • The expense of treatment limited its application to highly contaminated sites but on-site degradation of oxygen has reduced costs 18
  19. Biosparging • Hydrogen peroxide used on a number of sites but it can be toxic at low concentrations to MO • This process is similar to soil vapor extraction, which can be used for volatile contaminants 19
  20. Bioaugmentation • The addition of nutrients injected into contamination well below the surface can be used to stimulate the indigeneous microbial population. • This technique can be combined with the addition of specific MO 20
  21. Ex situ remediation techniques 21
  22. Ex situ remediation techniques • If the contaminated material is excavated it can be treated on or off site, which is often a more rapid method of de- contaminating the area • The techniques include – Composting – Biopile process – Bioreactors 22
  23. Composting • Solid-phase treatment carried out after extraction • Composting materials such as straw, bark and wood chips is mixed with the contaminated soil and piled into heaps • Process work in the same way as normal system which rise the temp to 60° C and above cause microbial activity • higher temp encourages the growth of thermophilic bacteria • Increased costs of this type of system restrict it to highly contaminated materials 23
  24. Composting • Organic materials added vegetables, fruit and garden waste • Added at a conc of 33-75% • Temp above 70° C achieved after 6-22 days of incubation, with turning every 7 days and 84-86% of the contamination was removed by day 40 compared with 35% in untreated soil. 24
  25. Biopile process • Soil heaped into piles within a lined area to prevent leaching • Piles covered with polythene and liquid nutrients applied to the surface • Aeration improved by applying suction to the base of the pile as in a composting system • Leachate collected by pipes at the base and recycled if necessary • Space limited 25
  26. Biopile process 26
  27. Bioreactors • Soil extracted from a contaminated site can be treated as a solid waste or a liquid leachate in bioreactors of various designs. • Control of parameters such as temp, pH, mixing and O₂ supply – improve degradation rates • Used for Solid waste slurries can be solid-bed, fluidized bed, and stirred tank bioreactors • When treating liquid leachates and contaminated ground water all those reactors – waste water treatment are used 27
  28. Bioreactors 28
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