2013
DOI: 10.1016/j.jhazmat.2013.07.062
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Investigation of the release of PAHs from artificially contaminated sediments using cyclolipopeptidic biosurfactants

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Cited by 33 publications
(13 citation statements)
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“…Although the least applied concentration of Tween80 is higher than the CMC of this surfactant (16 mg/L) [1], no significant desorption was observed. The reason for this occurrence is that in the soil surfactant solution system, due to the sorption of surfactant onto the soil particles, CMC would be greater than that of the liquid system, which is called effective CMC (CMC eff ) [5,15,23]. By increasing the surfactant concentration beyond the CMC eff , the sorbed amount of the surfactant reaches the stationary level and surfactant micelles begin to form in the aqueous phase, resulting in partitioning of PHE molecules within hydrophobic cores of the surfactant micelles [24].…”
Section: Resultsmentioning
confidence: 99%
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“…Although the least applied concentration of Tween80 is higher than the CMC of this surfactant (16 mg/L) [1], no significant desorption was observed. The reason for this occurrence is that in the soil surfactant solution system, due to the sorption of surfactant onto the soil particles, CMC would be greater than that of the liquid system, which is called effective CMC (CMC eff ) [5,15,23]. By increasing the surfactant concentration beyond the CMC eff , the sorbed amount of the surfactant reaches the stationary level and surfactant micelles begin to form in the aqueous phase, resulting in partitioning of PHE molecules within hydrophobic cores of the surfactant micelles [24].…”
Section: Resultsmentioning
confidence: 99%
“…Thanks to their low volatility, hydrophobic nature and high octanol-water partition coefficients (K ow ), these ubiquitous compounds are severely adsorbed onto the soil grains being very recalcitrant to degradation [1,3]. Therefore, PAHs-contaminated sites are potentially serious threats to both environmental resources and human health, duo to their bioaccumulation potential and extreme toxicity, mutagenicity and carcinogenicity impacts, posing the remediation of contaminated soils as a principal challenge [4,5]. In the last few decades, some environmental clean-up technologies including bioremediation, advanced chemical oxidation, electrochemical treatment, soil flushing, and soil washing have been applied for the remediation of PAHs-contaminated soils [6][7][8][9][10][11][12].…”
Section: Introductionmentioning
confidence: 99%
“…However, the bioremediation of PAHs is restricted by their low bioavailability, which results from their poor aqueous solubility, high hydrophobicity, and strong sorption to sediment or soil particles (Malik, Verma, Singh, & Singh, 2011). Enhancing the solubility of PAHs and promoting desorption from contaminated soil is a prerequisite for their bioremediation (Portet-Koltalo et al, 2013).…”
Section: Introductionmentioning
confidence: 99%
“…Previous studies have mostly focused on the sorption behaviour of polycyclic aromatic hydrocarbons (PAHs) on the sediments, including effects of oil type, mixing time, temperature, and salinity [15][16][17][18][19]. Nevertheless, only a few studies focused on the desorption of oil pollutants from oil-contaminated sediments.…”
Section: Introductionmentioning
confidence: 99%