Waste containment facilities are often composed of barriers such as liners,
grout curtains, and slurry walls. The primary design objective for such sy
stems is to mitigate against the release and transport of contaminants. It
is often necessary to quantify barrier effectiveness in order to conduct ri
sk and exposure assessments. The extent to which a barrier material is effe
ctive can be assessed using analytical methods, laboratory testing and fiel
d monitoring. Obviously, there is a great deal of time and expense associat
ed with both laboratory and field monitoring, making modeling an attractive
first alternative. There are, however, numerous solutions to the well-know
n advection-dispersion equation that vary in accuracy and applicability, de
pending on initial and boundary conditions. Moreover, most of the equations
formulated for transport through porous media were developed for use in aq
uifer rather than barrier material. Prudent model selection involves matchi
ng the conditions to be analyzed with the appropriate mathematical descript
ion.
In this article, five transport equations are analyzed and compared with la
boratory results and projected field conditions for the migration of Pb2+ t
hrough soil-bentonite. After 30 days of continuous source injection, measur
able concentrations of lead were only detected in the first 0.5 cm of a col
umn of soil-bentonite. All five solutions predicted approximately the same
level of penetration for the column tests; however, significant differences
emerged after extrapolation to field conditions. For barrier design purpos
es, the only equations recommended are Equation 3 (the complete solution fr
om Ogata and Banks [1961]) and Equation 6 (Crank's [1956] solution to Fick'
s Second Law).