Instituto de Recursos Naturales y Agrobiología de Sevilla (IRNAS), C.S.I.C., Avenida Reina Mercedes, 10, E-41012 Seville, Spain.
Univ Barcelona, Fac Biol, Dept Genet Microbiol & Stat, Diagonal 643, E-08028 Barcelona, Spain.
Sci Total Environ. 2019 Jun 10;668:790-796. doi: 10.1016/j.scitotenv.2019.03.056. Epub 2019 Mar 6.
The application of a rhamnolipid biosurfactant for enhanced solubilization and biodegradation of slowly desorbing polycyclic aromatic hydrocarbons (PAHs) in contaminated soils was determined in this study. The soil samples exhibited different levels of pollution and different bioremediation stages: the first soil originated from a creosote-polluted site, contained 4370 mg kg of PAHs and had not been bioremediated; the second soil was the same as the first but had received bioremediation treatment with nutrient amendment in biopiles for a period of 5 months and contained 580 mg kg of PAHs after this treatment; the third soil was treated by bioremediation for several years to reduce the concentration of PAHs to 275 mg kg . The kinetics of PAH desorption were determined to assess the magnitude of the slowly desorbing fractions present in the polluted soil and to optimize the biosurfactant effectiveness in terms of biodegradation. The soils that had been treated by bioremediation were enriched in slowly desorbing PAHs. The rhamnolipid at a concentration above its critical micelle concentration enhanced biodegradation in the soils that had been bioremediated previously. The measurement of residual concentrations of native PAHs showed the promoting effect of the biosurfactant on the biodegradation of the slowly desorbing fractions. Interestingly, benzo(a)pyrene was biodegraded in the soil that had been bioremediated for a long time. Rhamnolipid can constitute a valid alternative to chemical surfactants in promoting the biodegradation of slow-desorption PAHs, which is one of the most important problems in bioremediation, but the efficiency depends strongly on the bioremediation stage in which the biosurfactant is applied.
本研究旨在确定鼠李糖脂生物表面活性剂在增强污染土壤中缓慢解吸多环芳烃(PAHs)的增溶和生物降解中的应用。这些土壤样本具有不同程度的污染和不同的生物修复阶段:第一个土壤来自防腐油污染场地,含有 4370mg/kg 的 PAHs,尚未进行生物修复;第二个土壤与第一个相同,但在生物堆中添加营养物质进行了为期 5 个月的生物修复处理,处理后含有 580mg/kg 的 PAHs;第三个土壤经过多年的生物修复,将 PAHs 的浓度降低到 275mg/kg。通过测定 PAH 的解吸动力学,评估了污染土壤中存在的缓慢解吸部分的大小,并优化了生物表面活性剂在生物降解方面的效果。经过生物修复处理的土壤中富含缓慢解吸的 PAHs。鼠李糖脂在其临界胶束浓度以上的浓度增强了先前经过生物修复的土壤中的生物降解。残留的原生 PAHs 浓度的测量表明生物表面活性剂对缓慢解吸部分的生物降解具有促进作用。有趣的是,苯并(a)芘在经过长期生物修复的土壤中被生物降解。鼠李糖脂可以作为一种有效的化学表面活性剂替代品,促进缓慢解吸 PAHs 的生物降解,这是生物修复中最重要的问题之一,但效率强烈依赖于生物表面活性剂应用的生物修复阶段。