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Mass Transport of Pollutants

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Presentation on theme: "Mass Transport of Pollutants"— Presentation transcript:

1 Mass Transport of Pollutants

2 Dense Non-Aqueous Phase Liquids
NAPLs – Insoluble in water and Separate phase Dense NAPLs – More dense than water Chlorinated hydrocarbons Trichloroethylene-TCE Tetrachloroethylene-PCE Density increases with increasing halogenation Density difference of 0.1% causes sinking

3 Light Non-Aqueous Phase Liquids
Light NAPLs Lighter than water Petroleum hydrocarbons Oil Gasoline Density difference between water and NAPL of 1% can influence flow Low viscosity NAPLs migrate more rapidly than high viscosity NAPLs

4 Transport Processes Conservation of Mass for dissolved substances in groundwater Rate of change of mass = Flux of mass out – Flux of mass in ± gain or loss of mass due to reactions x y z Mass flux in Mass flux out

5 Solutes Conservative (nonreactive) Nonconservative (reactive)
Do not react with water or soil, do not biologically or radioactively decay Nonconservative (reactive)

6 Physical Processes Controlling Flux
Advection Solutes carried along by flowing groundwater Diffusion Transport by molecular diffusion Dispersion Transport by mechanical mixing

7 Solute Spreading

8 Advection Advection f = porosity vx = average velocity
Solutes carried along by flowing groundwater f = porosity vx = average velocity F = Advective flux = Total mass of solute which is carried across a unit area oriented normal to the bulk fluid motion

9 Diffusion Diffusion Molecular-based phenomenon
Net movement toward areas of lower concentration F = mass flux per unit area per unit time (M/L2/T) D* = apparent diffusion coefficient in soil (L2/T) C = solute concentration (M/L3) ∂C/∂x = concentration gradient (M/L3/L)

10 Dispersion Mechanical Dispersion
Transport by mechanical mixing F = mass flux per unit area per unit time (M/L2/T) Dx = dispersion coefficient (L2/T) C = solute concentration (M/L3) ∂C/∂x = concentration gradient (M/L3/L)

11 Advection-Dispersion Equation
F = mass flux per unit area per unit time (M/L2/T) Dx = dispersion coefficient (L2/T) C = solute concentration (M/L3) ∂C/∂x = concentration gradient (M/L3/L)

12 Mass Flux x y z Mass flux in Mass flux out

13 Mass Balance Equation Mass accumulation

14 Solution Solution

15 Error Function

16 Error Function Values Homework: Problems 881 and 884

17 Groundwater Monitoring

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20 T08_10_04


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