Sánchez-Martín M J, Dorado M C, del Hoyo C, Rodríguez-Cruz M S
Instituto de Recursos Naturales y Agrobiología, CSIC, Apdo, 257, 37071 Salamanca, Spain.
J Hazard Mater. 2008 Jan 15;150(1):115-23. doi: 10.1016/j.jhazmat.2007.04.093. Epub 2007 Apr 24.
Adsorption of three surfactants of different nature, Triton X-100 (TX100) (non-ionic), sodium dodecylsulphate (SDS) (anionic) and octadecyltrimethylammonium bromide (ODTMA) (cationic) by four layered (montmorillonite, illite, muscovite and kaolinite) and two non-layered (sepiolite and palygorskite) clay minerals was studied. The objective was to improve the understanding of surfactant behaviour in soils for the possible use of these compounds in remediation technologies of contaminated soils by toxic organic compounds. Adsorption isotherms were obtained using surfactant concentrations higher and lower than the critical micelle concentration (cmc). These isotherms showed different adsorption stages of the surfactants by the clay minerals, and were classified in different subgroups of the L-, S- or H-types. An increase in the adsorption of SDS and ODTMA by all clay minerals is observed up to the cmc of the surfactant in the equilibrium solution is reached. However, there was further TX100 adsorption when the equilibrium concentration was well above the cmc. Adsorption constants from Langmuir and Freundlich equations (TX100 and ODTMA) or Freundlich equation (SDS) were used to compare adsorption of different surfactants by clay minerals studied. These constants indicated the surfactant adsorption by clay minerals followed this order ODTMA>TX100>>SDS. The adsorption of TX100 and ODTMA was higher by montmorillonite and illite, and the adsorption of SDS was found to be higher by kaolinite and sepiolite. Results obtained show the influence of clay mineral structure and surfactant nature on the adsorption capacity of surfactants by clays, and they indicate the interest to consider the soil mineralogical composition when one surfactant have to be selected in order to establish more efficient strategies for the remediation of soils and water contaminated by toxic organic pollutants.
研究了三种不同性质的表面活性剂,即 Triton X-100(TX100)(非离子型)、十二烷基硫酸钠(SDS)(阴离子型)和十八烷基三甲基溴化铵(ODTMA)(阳离子型)在四种层状(蒙脱石、伊利石、白云母和高岭石)和两种非层状(海泡石和凹凸棒石)粘土矿物上的吸附情况。目的是加深对表面活性剂在土壤中行为的理解,以便这些化合物可能用于受有毒有机化合物污染土壤的修复技术。使用高于和低于临界胶束浓度(cmc)的表面活性剂浓度获得吸附等温线。这些等温线显示了表面活性剂在粘土矿物上的不同吸附阶段,并被归类为 L 型、S 型或 H 型的不同亚组。观察到所有粘土矿物对 SDS 和 ODTMA 的吸附在达到平衡溶液中表面活性剂的 cmc 之前都会增加。然而,当平衡浓度远高于 cmc 时,TX100 会有进一步的吸附。使用朗缪尔方程和弗伦德利希方程的吸附常数(TX100 和 ODTMA)或弗伦德利希方程(SDS)来比较所研究的粘土矿物对不同表面活性剂的吸附。这些常数表明粘土矿物对表面活性剂的吸附顺序为 ODTMA>TX100>>SDS。蒙脱石和伊利石对 TX100 和 ODTMA 的吸附较高,而高岭石和海泡石对 SDS 的吸附较高。所得结果表明粘土矿物结构和表面活性剂性质对粘土吸附表面活性剂能力的影响,并且它们表明在选择一种表面活性剂以建立更有效的受有毒有机污染物污染的土壤和水的修复策略时,考虑土壤矿物组成的重要性。