Effects of chelating agent (CA) on the removal of polychlorinated biphenyls (PCBs) from capacitor-oil-contaminated soil slurry were investigated through homogeneous Fenton treatment at natural soil pH. Among the five CAs used, promoting PCB removal by sodium pyrophosphate (SP) was the strongest, followed by the promoting effect of ethylenediamine-N,N'-bis(o-hydroxyphenyl) acetic acid (EDDHA). When the Fe2+ concentration was 50 mM, the optimal Fe2+/SP/H2O2 and Fe2+/EDDHA/H2O2 molar ratios were 1/1/20 and 1/0.5/20, respectively; the corresponding efficiencies of 48 h PCB degradation at 63.9 mg kg(-1) initial PCB concentration in soil slurry were 87.5% and 77.1%, respectively. The efficiency of H2O2 oxidation was significantly higher than that of Na2S2O8 oxidation, regardless of activation by either Fe2+-SP complex or Fe2+-EDDHA complex. The final pH of the Fe2+/EDDHA/H2O2 system was markedly lower (2.7) than the initial soil pH (7.6), and that of the Fe2+/SP/H2O2 system was slightly lower (about 6.6) after 48 h of reaction. Electron paramagnetic resonance detection directly showed that (OH)-O-center dot is the primary species involved in PCB degradation whether CA was added to the Fenton reaction system or not. The probe test revealed that PCB degradation in the Fe2+/SP/H2O2 system is mainly attributed to (OH)-O-center dot and that it is ascribed to the combined actions of (OH)-O-center dot and O-2(center dot-) in the Fe2+/EDDHA/H2O2 system. Results of this study indicate that CA-enhanced Fenton oxidation is an effective and practical means of remediation of soil heavily contaminated with PCBs.