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Surfactant-modified native soil in the treatment of oil field (Nimr) produced water

机译:表面活性剂改性的原生土壤在油田(Nimr)采出水的处理中

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In this study, we investigated the possibility to use surfactant-modified and unmodified native sand (Oman) for the treatment of oil field (Nimr) produced water. Dodecyltrimethylammonium (DDTMA) bromide was used to modify the sand properties. In our approach, surfactant was added to the contaminated water and the resulting aqueous surfactant solution was forced to percolate through the column packed with native soil. Thus, in this approach, soil modification by the surfactant molecules occurs during the water treatment process. Rejections of the crude oil aromatic components were estimated using a new and simple approach based on the measured total fluorescence emission ratio A_p/A_0, where A_p is the total fluorescence area of the permeate and A_0 the total fluorescence area of the untreated water. Our results from the packed column with unmodified native sand showed substantial rejection of aromatic hydrocarbons (~ 85%) only for the first individual 100 mL permeate sample collected. As the cumulative volume of permeate increases up to 1000 mL, the rejection decreases to less than 10%. When surfactant was added to the feed (contaminated Nimr water) at 1CH M (below the surfactant CMC), complete rejection occurred only with the first individual 100 mL permeate sample collected, followed by a decrease in the rejection to about 45% rejection as the cumulative permeate volume reached 1000 mL On the other hand, when e surfactant was added above its CMC (5×10~(-4) M and 1×10~(-3) M), all individual 100 mL (10 separate individual 100 ml samples) were practically free of aromatics (-100% rejection). Thus, complete rejections occurred only at and above the surfactant critical micelle concentration. This concentration-dependent rejection of the aromatics was associated to the concentration-dependence of the surfactant onto the substrate surface.
机译:在这项研究中,我们调查了使用表面活性剂改性和未改性天然砂(阿曼)处理油田(Nimr)采出水的可能性。使用十二烷基三甲基铵(DDTMA)溴化物来改善砂子的性能。在我们的方法中,将表面活性剂添加到受污染的水中,然后迫使所得的表面活性剂水溶液渗透过充满天然土壤的色谱柱。因此,在这种方法中,在水处理过程中发生了表面活性剂分子对土壤的改性。基于测得的总荧光发射比A_p / A_0,使用一种新的简单方法来估算原油芳香成分的排斥率,其中A_p是渗透液的总荧光面积,A_0是未处理水的总荧光面积。我们用未经改性的天然沙子填充柱得到的结果表明,仅对于收集到的第一个单独的100 mL渗透物样品,芳香烃(〜85%)才被排除。当渗透物的累积体积增加到1000 mL时,截留率降低到小于10%。当以1CH M(在表面活性剂CMC下方)将表面活性剂添加到进料(受污染的Nimr水)中时,只有在收集到的第一个单独的100 mL渗透液样品中,才发生完全排斥,然后将其降低至约45%的排斥累积渗透量达到1000 mL另一方面,当在其CMC上方添加表面活性剂(5×10〜(-4)M和1×10〜(-3)M)时,所有单独的100 mL(10个单独的100毫升样品)几乎不含芳族化合物(-100%排斥)。因此,仅在表面活性剂临界胶束浓度及以上才发生完全排斥。芳族化合物的这种浓度依赖性排斥与表面活性剂在基材表面上的浓度依赖性相关。

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