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Multiphase Field-scale Modeling: Brine Transport. Ann Cook Per Hatlevik Jonathan Levine Brice Loose Keegan Roberts Amber Sallerson Katy Schulte Martina Vlckova Thomas Willingham. Introduction to DNAPLs. Types Sources Behavior. PCE, TCE, DCE, VC, CT, CF, DCM, TCA.
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Multiphase Field-scale Modeling: Brine Transport Ann Cook Per Hatlevik Jonathan Levine Brice Loose Keegan Roberts Amber Sallerson Katy Schulte Martina Vlckova Thomas Willingham
Introduction to DNAPLs • Types • Sources • Behavior PCE, TCE, DCE, VC, CT, CF, DCM, TCA
Introduction to DNAPLs • Long lived • Difficult to remove • Health Hazards • Liver problems • Increased risk of cancer • Nervous system, or circulatory problems1
Brine Treatment Technology • How does it work? • Mobilization of the NAPL • Increase Gravimetric Forces • Decrease Capillary Trapping Forces
Brine Treatment Technology • sn-a = NAPL-aqueous interfacial tension • r =effective pore size • rn= NAPL density • ra= aqueous phase density • g = gravitational acceleration • l = characteristic length of NAPL pool in vertical direction
Area of Remediation Sheet-piles Impermeable Layer (e.g., clay) Plan View Profile View Brine Treatment Technology • How does it work? • Closed system on 5 sides
Brine Treatment Technology • How does it work? No Flow Boundary No Flow Boundary
Brine Treatment Technology • How does it work? Pump in Brine Layer
Brine Treatment Technology • How does it work? Lower Water Table
Brine Treatment Technology • Gravimetric Forces Removal of DNAPL
Brine Treatment Technology • How does it work?
Brine Treatment Technology • How does it work? Removal of DNAPL
Brine Treatment Technology • How does it work?
Brine Treatment Technology • How does it work? Remove Brine <1% Original DNAPL Mass
Brine Treatment Technology • How does it work? <1% Original = Meet DNAPL Mass Standards
Brine Treatment Technology • Why is it novel? • $$ Cheaper $$ • Higher rates of removal than current technologies Pump and Treat Natural Attenuation
Possible Instabilities in the System • Physical • Density (changes and/or differences) • Excessive Surfactant Concentration bypass • Pore Clogging • Model • Fingering • Gravity - Rayleigh
Rayleigh-Taylor Instability Brine • Initial density stratified domain • Unstable system (small perturbations) • Occur in model and physical system Ground Water
Rayleigh Number • Dimensionless Number • Ratio
SUTRA • Code written by USGS • Simulates single phase fluid flow and transport in the subsurface • Uses a combination of finite-element and finite difference methods to solve a series of equations
Conservation Equations • Species Balance Equation • Species-Summed Flow Equation
SUTRA Transport Math Magic
SUTRA Fluid Flow Species Summed Flow Equation Darcy’s Law Math Magic
Requirements for SUTRA DL < 4aL Pe < 2 • DL = local distance between sides of an element measured in the direction parallel to local flow • aL = longitudinal dispersivity
SUTRA Goal • To model a freshwater system where we inject brine • 3D model • Relatively small in the y-direction • Visualize system instabilities • Removal of brine from system
Simulations Ran • Brine slumping model • Fully saturated fresh water system with brine injection • Unsaturated brine injection • Multiple well configurations
Example Problem: Slumping brine interface High frequency spatial hydraulic conductivity which admits an analytic solution in the case that the vertical scale is much less that the horizontal (H << R), and a constant hydraulic conductivity (Kc)
Homogenization permits approximation of K(x,z,t) as a constant that captures the variability Homogenized equations compare well with the accepted numerical solution. High frequency variations are absent.
Evaluate Instabilities Injection Wells Extraction Well
Fingering Fingering due to viscous instability