The mass transfer of gasoline constituents [benzene, toluene, ethylben
zene, xylenes (BTEX), and naphthalene] to air during laboratory-simula
ted soil vapor extraction (referred to here as soil venting) was deter
mined. Soil venting was conducted on laboratory-packed columns brought
to residual water then residual gasoline saturations. The columns con
tained either a sandy, low organic soil (0.10% organic carbon), a sand
y organic soil (1.65% organic carbon), or glass beads. Gasoline-air pa
rtitioning at the start of soil venting was experimentally determined
to be adequately described by Raoult's law for many gasoline constitue
nts of interest. The application of the local equilibrium assumption u
sed to describe the mass transfer of gasoline constituents from the re
sidual gasoline to air during soil venting was investigated using: (1)
Experimental techniques such as reduction of air flow rate: flow-inte
rruption and discrete sampling of soil following soil venting; and (2)
a local-equilibrium-based model employing Raoult's law to describe ga
soline-air partitioning. The local equilibrium assumption was shown to
be valid for describing the mass transfer of various gasoline constit
uents until such time when the constituent was nearly depleted from th
e non-aqueous-phase liquid gasoline (NAPL). Mass transfer of constitue
nts became rate-limiting when the constituent was depleted from the re
sidual gasoline. The effect of soil organic matter content was only sl
ightly apparent at this time, as evidenced by the higher benzene and t
oluene air concentration in the effluent of columns containing the san
dy organic soil.