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Soil Vapor Extraction Limitations and Enhancements

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Title: Soil Vapor Extraction Limitations and Enhancements


1
Soil Vapor Extraction Limitations and Enhancements
  • LeeAnn Racz
  • AgE 558
  • Semester Project
  • April 2001

2
Outline
  • Theory
  • SVE Mass Removal Performance
  • Gas Extraction Methods
  • Application
  • Limitations to SVE
  • Enhancements to SVE
  • Remaining Uncertainties/Challenges

3
Theory
  • Removes soil gas under vacuum from soil matrix
  • Mass transfers from aqueous and sorbed phases to
    gas phase in order to re-establish equilibrium
  • Model assumes mass transfer between gas and solid
    phases occurs via continuous film of water
    (wetting fluid)

4
Mass Transfer Processes in the Vadose Zone
(Armstrong et al. 1994)
Advecting Air
Air/Water Partitioning (Volatilization)
Dissolved Contaminant
Sorbed Contaminant
Soil Moisture
Soil Grain
Water/Solid Partitioning (Desorption)
5
SVE Mass Removal Performance
  • First Stage
  • Removes pure product
  • System in equilibrium
  • High off-gas concentrations
  • Relatively short duration
  • Henrys law dominates
  • High organic content can have partitioning
    between liquid and solid phases in equilibrium

6
SVE Mass Removal Performance
  • Henrys law

Pi HiCi or Hi CwCa where Pi partial
pressure in gas phase Ci and Cw concentration
in aqueous phase Hi Henrys law constant for
phase partitioning of i Ca concentration in gas
phase
7
SVE Mass Removal Performance
  • Partitioning between liquid and solid phases
  • Expressed as linear Freundlich isotherm
  • Valid for soils with gt0.1 organic carbon

Kd Cs/Cw and Kd foc/Koc where Kd
distribution coefficient Cs concentration in
sorbed phase foc mass fraction of organic
carbon Koc organic carbon partitioning
coefficient
8
SVE Mass Removal Performance
  • Second Stage
  • Transition from first to third stages
  • System is in non-equilibrium
  • Quickly declining mass removal rates

9
SVE Mass Removal Performance
  • Third Stage
  • Also in non-equilibrium
  • Partitioning between soil gas, soil moisture and
    soil solids limit the mass transfer rate to
    mobile gas pathways
  • Non-zero asymptote

10
SVE Mass Removal Performance
  • Non-equilibrium mass transfer (second and third
    stages)
  • Rate limiting factors in mass transfer process
  • Modeled as first-order kinetic mass transfer
    relationships
  • Diffusive mass transfer between air and water
    driven by concentration gradient between average
    concentration in water phase and equilibrium
    concentration at water/air interface
  • Kinetically limited desorption from soil grains
    to water phase

11
Gas Extraction Methods
  • Active
  • Involves introducing fresh air into soil
  • Apply vacuum by mechanical means to draw soil gas
    from soil matrix
  • Passive
  • Screened well installed
  • Open to atmosphere
  • Gas flows from soil matrix out through open well
    when subsurface gas pressure greater than
    barometric pressure

12
Limitations to SVE
  • Well suited for
  • Vapor removal from moist sand and granular soils
  • Soils with increased gas permeability
  • Removing VOCs and LNAPLs

13
Limitations to SVE
  • Not so well suited for
  • Removing contaminants from capillary fringe
  • Low relative permeability to soil gas flow makes
    diffusion the rate-limiting process
  • Sites with high water tables
  • Mixed contamination
  • Includes nonvolatile compounds and DNAPLs
  • Sites without sufficient moisture
  • If too dry, increases sorption capacity of soil

14
Enhancements to SVE
  • Synergistic Effects
  • Pump and treat ground water
  • Leaves dewatered area treatable by SVE
  • SVE vacuum produces air flow
  • Enhances effects of aerobic microbial activity
  • Air sparging
  • Injects air into ground water and extracts
    volatile portion to unsaturated zone
  • Extracts gas and controls vapor migration

15
Enhancements to SVE
  • Soil Heating
  • Increases volatility of contaminant to gas phase
  • Reduces mass transfer limitations in
    non-equilibrium conditions
  • Useful for removing chlorinated compounds and
    compounds with higher boiling points
  • Methods
  • Hot air
  • Electrical heating
  • Microwave energy

16
Enhancements to SVE
  • Pulse Pumping
  • Theory turn off vacuum at tailed portion of
    effluent curve and allow air phase concentrations
    to recover, then reapply vacuum
  • Intended to give lower energy costs and effluent
    treatment costs
  • However, slow but continuous pumping gives best
    performance

17
Enhancements to SVE
  • Passive SVE
  • Cap well with check valve to prevent air from
    flowing into subsurface through well
  • Lightweight ball in conical seat
  • Solenoid valve
  • Install surface cover around well
  • Prevents short-circuiting adjacent to well to
    increase horizontal flow to well
  • Prevents clean air from entering subsurface
    diluting contaminant concentrations
  • Increases differential between surface and
    subsurface gas pressures

18
Remaining Uncertainties/Challenges
  • Difficult to use in removing DNAPLs and other
    recalcitrant compounds
  • Difficult to use in certain soil types
  • Low porosity
  • High moisture content
  • Capillary fringe

19
Remaining Uncertainties/Challenges
  • Combine with other methods for synergistic
    effects
  • Nonzero asymptotic characteristic of
    nonequilibrium
  • Better measuring techniques to obtain data for
    better designs
  • Uncertainties in heterogeneous media
  • Otherwise, rely on further refined curve-fitted
    models

20
  • E-mail
  • leeann.racz_at_osan.af.mil
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