摘要
An effective Fenton oxidation technology was developed to degrade PAHs in the soil, and fluorene (FLU), phenanthrene (PHE), fluoranthene (FLA) and pyrene (PYR) were selected as primary pollutants. This research presented a systematic approach to optimize the key operational parameters, such as reaction time, H 2 O 2 concentration, Fe 2+ /H 2 O 2 addition ratio, pH value, and soil-water ratio, those factors altogether affected the generation of • OH and the overall degradation efficiency of PAHs. The optimized parameter combination of Fenton technology suitable for PAHs degradation in complex soil environments was proposed. The key parameters were as follows: soil-water ratio was 2:1, pH was 3, H 2 O 2 concentration was 11 % of the total system, Fe 2+ /H 2 O 2 addition ratio was 1/8, and reaction time was 24 h. The degradation percentages for FLU, PHE, FLA and PYR were 75.4 %, 66.2 %, 60.8 % and 93.7 % in this optimized system, respectively. As the reaction time increased, the degradation efficiency of PAHs by Fenton technology reached the maximum until it became stable or slightly decreased. Appropriate H 2 O 2 concentration and Fe 2+ /H 2 O 2 addition ratio were conducive to the maximum generation of • OH, thus improving the degradation efficiency of PAHs. The pH value significantly influenced the degradation of PAHs, and the soil-water ratio had important effects on the Fenton oxidation process. By optimizing these conditions, a more thorough and profound assessment of the Fenton technology's applicability in treating actual-world PAHs-polluted soils was achievable, and it was expected to reduce the restoration cost. Meanwhile, it also contributed to the development of more efficient and sustainable soil remediation strategies.
危险品化学品经营许可证(带存储)