Removal of hydrophobic organic contaminants (HOCs) from saturated low-perme
ability subsurface environments using a solubility-enhanced electrokinetic
remediation process is demonstrated for a model system. Phenanthrene, hydro
xypropyl-beta-cyclodextrin (HPCD), and kaolinite were selected as a represe
ntative HOC, HOC solubility-enhancing agent, and model clay soil, respectiv
ely. Electrokinetic (EK) column experiments were conducted under various op
erating conditions, and the results were interpreted in terms of the EK pro
perties and expected phenanthrene solubilization of the test systems. No si
gnificant effects of HPCD on the EK properties of kaolinite were observed.
Initial pore solution pH values dictated the initial electroosmotic flow (E
OF) and charge flow rates through the test samples. However, with increasin
g EK operating times, low pH values (i.e., near or below the point of zero
charge of kaolinite) dominated over most of the column length in unbuffered
systems, thereby decreasing the EOF and charge flow rates with time. To mi
nimize these adverse effects, pH control of the anode reservoir with a Nar
CO3 buffer was used to keep EOF and charge flow rates high. EK experiments
using HPCD solutions showed greater phenanthrene removal from the kaolinite
samples, and the removal efficiency depended on the HPCD concentration use
d. Longer EK operating times without pH control were generally not benefici
al for removing phenanthrene because of the low EOF rates obtained after 3
days. The best overall phenanthrene removal was obtained by flushing the an
ode reservoir with a high HPCD concentration prepared in the Na2CO3 buffer
solution. The results obtained from this preliminary study show that an EK
process combined with HPCD flushing and pH buffering may be a good remediat
ion alternative for removing HOCs from low-permeability subsurface environm
ents.