Knowledge of the relationship between D(P)/D0 (diffusion coefficient i
n soil divided by diffusion coefficient in free air) and the volumetri
c soil-air content, epsilon, is important when modeling gaseous moveme
nt of volatile organic compounds (VOCs) in soils. The effective diffus
ion (i.e., diffusion and retardation) of trichloroethylene (TCE), tolu
ene and freon in Yolo silt loam (fine-silty, mixed, nonacid, thermic T
ypic Xerorthent) were measured in a two-chamber diffusion apparatus. T
he experiments were conducted on packed soil cores over a range of wat
er contents. Vapor retardation factors were calculated from soil param
eters and equilibrium partition coefficients. Partition coefficients w
ere measured in batch experiments. It was found that for water content
s higher than four molecular layers of water surface coverage, solid/v
apor partition coefficients, K(D)', were consistent with values predic
ted by Henry's Law constants (K(H)), and squeous/solid partition coeff
icients, K(D). For less than four molecular layers of water, sorption
increased by orders of magnitude. The vapor retardation factors, along
with the measured effective diffusion, allowed a calculation of diffu
sion coefficients (D(P)) for the investigated species by using the ana
lytical solution to diffusion in a two-chamber apparatus. Values of th
e ratio D(P)/D0 were generally higher than the values predicted by the
Millington-Quirk equation, and lower than the values predicted by the
Penman equation. Compared with the nonreactive tracer freon, D(P)/D0
values for TCE and toluene agreed very well for higher water contents.
Values obtained for air-dry soil, however, were under-predicted. The
experimental work for determination of the effective diffusion of reac
tive tracers can, therefore, for sufficiently high water contents be l
imited to the determination of D(P)/D0-epsilon relations for a nonreac
tive tracer and measurement of K(D), K(D)', and K(H) values for the re
active tracers.