IntroductionPolycyclic aromatic hydrocarbons (PAHs) are widely distributed hydrophobic organic contaminants (HOCs) and accumulate in soil that has been contaminated with crude oil, creosote, or coal tar. PAHs are also generated and dispersed into the environment by fossil fuel combustion, wood treatment processes, automobile exhausts, and waste incineration (Wilson and Jones, 1993). Because of their widespread distribution and their toxicity and mutagenicity, PAHs are listed as priority pollutants, and remediation of soils contaminated with PAHs is of great importance. Phytoremediation is a promising alternative approach to soil remediation due to its convenience, cost-effectiveness and environmental acceptability. The HOCs in soil usually exhibit low bioavailability to both microorganisms and plants due to their strong affinity to the soil matrix, especially to soil organic matter (Chen et al., 2005), which limits the application of phytoremediation. Solubilization agents such as the surfactant Triton X-100 have been added to soil to enhance the release of HOCs from the sorbed phase and, thereby, to increase their aqueous concentrations and bioavailability (Zhou and Zhu, 2005). Although addition of surfactants has been explored in the cleanup of contaminated soils (Zhu et al., 2003), there are few reports of their application in phytoremediation.Arbuscular mycorrhiza (AM) is a ubiquitous association between soil fungi and the roots of most herbaceous plant