Standard measurements of solute sorption to sediments are typically made on
the <2 mm sediment fraction. This fraction is used by researchers to stand
ardize the method and to ease experimental protocol so that large labware i
s not required to accommodate the gravel fraction (>2 mm particles). Since
sorption is a phenomenon directly related to surface area, sorption measure
ments based on the <2 mm fraction would be expected to overestimate actual
whole-sediment values for sediments containing gravel. This inaccuracy is a
problem for ground water contaminant transport modelers who use laboratory
-derived sorption values, typically expressed as a distribution coefficient
s (Kd), to calculate the retardation factor (Rf), a parameter that accounts
for solute-sediment chemical interactions. The objectives of this laborato
ry study were to quantify the effect of gravel on strontium Kd and Rf value
s and to develop an empirical method to calculate gravel-corrected Kd value
s for the study site (Hanford Site in Richland, Washington). Three gravel c
orrections, Kd(gc) values, were evaluated: a correction based on the assump
tion that the gravel simply diluted the Kd(< 2mm) and had no sorption capac
ity (Kd(gc),(g=0)), a correction based on the assumption that the Kd of the
intact sediment (Kd(tot)) was a composite of the Kd(< 2mm) and the Kd(> 2m
m) (Kd(gc,g=x)), and a correction based on surface area (Kd(gc,surf)). On a
verage, Kd(< 2mm) tended to overestimate Kd(tot) by 28% to 47%; Kd(gc,g=x)
overestimated Kd(tot) by only 3% to 5%; and Kd(gc,g=0) and Kd(gc,surf) unde
restimated Kd(tot) by 10% to 39%. Kd(gc,g=x) provided the best estimate of
actual values (Kd(tot)); however, Kd(gc,g=0) was appreciably easier to acqu
ire. Although other contaminants will likely have different gravel-correcti
on values, these results have important implications regarding the traditio
nal approach to modeling contaminant transport which uses Kd(< 2mm) values.
Such calculations may overestimate the tendency of gravel-containing sedim
ents to retard contaminant migration.