Piskonen Reetta, Itävaara Merja
VTT Biotechnology, PO Box 1500, 02044, Espoo, Finland.
Appl Microbiol Biotechnol. 2004 Oct;65(5):627-34. doi: 10.1007/s00253-004-1679-2. Epub 2004 Aug 4.
The efficiency of several chemical treatments as potential enhancers of the biodegradation of polycyclic aromatic hydrocarbons (PAHs) in contaminated soil was evaluated by analyzing the mineralization of 14C-labeled phenanthrene, pyrene, and benzo(a)pyrene. The effect of nonionic surfactants with Fenton oxidation and combinations of surfactants with the Fenton oxidation was evaluated in a microtiter plate assay. The surfactants selected for the study were Tween 80, Brij 35, Tergitol NP-10, and Triton X-100. The addition of Fenton's reagent significantly enhanced the mineralization of pyrene at the two concentrations studied: 2.8 M H2O2 with 0.1 M FeSO4 and 0.7 M H2O2 with 0.025 M FeSO4. Phenanthrene mineralization was also positively induced by the Fenton treatments. However, none of the treatments had a significant effect on benzo(a)pyrene mineralization. Surfactant additions at concentrations of 20% and 80% of the aqueous critical micelle concentration did not significantly affect the mineralization rates. When surfactant addition was combined with the Fenton oxidation, reduced mineralization rates were obtained when compared with mineralization after Fenton's treatment alone. The results indicate that the addition of Fenton's reagent may enhance the mineralization of PAHs in contaminated soil, whereas the addition of surfactants has no significant beneficial effect. The efficiency of the Fenton oxidation may decrease when surfactants are added simultaneously with Fenton's reagent to contaminated soil.
通过分析14C标记的菲、芘和苯并(a)芘的矿化情况,评估了几种化学处理方法作为污染土壤中多环芳烃(PAHs)生物降解潜在增强剂的效率。在微量滴定板试验中评估了非离子表面活性剂与芬顿氧化法以及表面活性剂与芬顿氧化法组合的效果。本研究选择的表面活性剂为吐温80、月桂醇聚醚35、壬基酚聚氧乙烯醚10和曲拉通X-100。在所研究的两种浓度下,添加芬顿试剂均显著提高了芘的矿化率:2.8M过氧化氢与0.1M硫酸亚铁以及0.7M过氧化氢与0.025M硫酸亚铁。芬顿处理也对菲的矿化有正向诱导作用。然而, 这些处理方法对苯并(a)芘的矿化均无显著影响。以水临界胶束浓度的20%和80%添加表面活性剂对矿化率无显著影响。当表面活性剂添加与芬顿氧化法相结合时,与单独芬顿处理后的矿化相比,矿化率降低。结果表明,添加芬顿试剂可能会提高污染土壤中PAHs的矿化率,而添加表面活性剂则没有显著的有益效果。当表面活性剂与芬顿试剂同时添加到污染土壤中时,芬顿氧化的效率可能会降低。