Batch and dynamic leaching experiments were conducted to evaluate the influ
ence of clay mineralogy and soil organic matter (SOM) present in two highly
weathered, surface and subsurface soil materials on Pb sorption and subseq
uent extraction using ethylenediaminetetraacetic acid (EDTA) and carboxymet
hyl beta -cyclodextrin (CMCD). Saturated soil columns were leached with an
acidic Pb solution to simulate a contamination event, followed by injection
of artificial groundwater (AGW) at constant velocity, Greater Pb retardati
on was observed within the surface soil compared to the subsurface soil mat
erial, and a significant increase in effluent turbidity was observed coinci
dent with the Pb breakthrough in the subsurface soil material. Electrophore
tic, thermo-gravimetric, and X-ray diffraction analysis of the resulting su
spension suggested that the presence of strongly adsorbing Pb2+ and excess
H+ increased the positive charge on amphoteric mineral surfaces and reduced
the negative charge on clay minerals, which induced selective dispersion a
nd transport of Fe oxides. In contrast, no increase in turbidity was observ
ed for the surface soil following Pb injection. While only 30% of adsorbed
Pb was mobilized from contaminated subsurface soil material, less than 10%
of adsorbed Ph was extracted from surface soil when Pb-contaminated soil co
lumns were flushed with AGW. Following leaching with AGW, extraction soluti
ons containing either 0.37 g L-1 (1 mM) EDTA or 10 g L-1 CMCD were applied
to extract the residual bound Pb. Nearly 100% of residual Ph was extracted
from the surface soil by EDTA as compared to about 56% removal by CMCD unde
r similar conditions. About 80% of residual Ph was removed by EDTA from the
Pb-contaminated subsurface material, but less than 2% of residual Pb was e
xtracted by CMCD under similar conditions.