Influence of clay mineral structure and surfactant nature on the adsorption capacity of surfactants by clays.
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.
Sánchez-Martín
M J
MJ
Instituto de Recursos Naturales y Agrobiología, CSIC, Apdo, 257, 37071 Salamanca, Spain. mjesusm@usal.es
Dorado
M C
MC
del Hoyo
C
C
Rodríguez-Cruz
M S
MS
D000327:Adsorption; D000473:Alkanes / Q000737:chemistry; D000538:Aluminum Silicates / Q000737:chemistry*; D001546:Bentonite / Q000737:chemistry; D000077215:Clay; D007616:Kaolin / Q000737:chemistry; D017616:Magnesium Compounds / Q000737:chemistry; D017633:Magnesium Silicates / Q000737:chemistry; D008903:Minerals / Q000737:chemistry; D017830:Octoxynol / Q000737:chemistry; D000644:Quaternary Ammonium Compounds / Q000737:chemistry; D017655:Silicon Compounds / Q000737:chemistry; D012967:Sodium Dodecyl Sulfate / Q000737:chemistry; D012989:Soil Pollutants / Q000032:analysis / Q000737:chemistry*; D013057:Spectrum Analysis; D013501:Surface-Active Agents / Q000737:chemistry*
D000473:Alkanes; D000538:Aluminum Silicates; D017616:Magnesium Compounds; D017633:Magnesium Silicates; D008903:Minerals; D000644:Quaternary Ammonium Compounds; D017655:Silicon Compounds; D012989:Soil Pollutants; D013501:Surface-Active Agents; C517971:muscovite; C518260:octadecyltrimethylammonium bromide; C099089:illite; D001546:Bentonite; D007616:Kaolin; D012967:Sodium Dodecyl Sulfate; D017830:Octoxynol; C001671:magnesium trisilicate; D000077215:Clay; C026325:attapulgite