Surfactants above their critical micelle concentration
can solubilize hydrophobic contaminants into their
micelles. This process enhances the apparent
solubility
of contaminants such as hydrocarbons and, therefore,
also their desorption from soils. Conceivably, in the
absence of any inhibitory effects, such surfactants
may enhance the biodegradation of the hydrocarbon.
Through a set of screening experiments, a series
of nonionic surfactants were identified that do not
inhibit the biodegradation of phenanthrene. A
mathematical model was formulated to describe the
interaction of the biomass−contaminant−water−surfactant system. Assumptions that the model formulation is based on are that the phenanthrene in
solution, partitioned into the micellar phase and sorbed
onto the biomass and other solid surfaces,is at
equilibrium and that these equilibria can be described
by simple partition coefficients. It was also assumed
that the presence of the surfactant does not affect
the biochemical characteristics of the biomass. An
effective bioavailable micellar-phase concentration of
phenanthrene was defined. The model simulates
experimental data well, indicating that a fraction of the
micellar-phase phenanthrene is directly bioavailable.
For three of the surfactants tested (Triton N101,
Triton X100, and Brij 30), the micellar-phase bioavailable
fraction of phenanthrene decreased with an increasing surfactant concentration. For Brij 35, it was
found that the fraction of the phenanthrene associated
with the micellar phase was not directly bioavailable.