Rodríguez-Cruz M S, Sánchez-Martín M J, Sánchez-Camazano M
Instituto de Recursos Naturales y Agrobiología de Salamanca, CSIC, Apdo 257, 37071 Salamanca, Spain.
J Environ Qual. 2004 May-Jun;33(3):920-9. doi: 10.2134/jeq2004.0920.
A study of the desorption of atrazine (1-chloro-3-ethylamino-5-isopropylamino-2,4,6-triazine) and linuron [1-methoxy-1-methyl-3-(3,4-dichlorophenyl)urea] adsorbed on soils with different organic matter (OM) and clay contents was conducted in water and in the presence of the non-ionic surfactant Triton X-100 at different concentrations. The aim was to gain insight into soil characteristics in surfactant-enhanced desorption of herbicides from soils. Adsorption and desorption isotherms in water, in all Triton X-100 solutions for atrazine, and in solutions of 0.75 times the critical micelle concentration (cmc) and 1.50cmc for linuron fit the Freundlich equation. All desorption isotherms showed hysteresis. Hysteresis coefficients decreased for linuron and increased or decreased for atrazine in Triton X-100 solutions. These variations were dependent on surfactant concentration and soil OM and clay contents. In the soil-water-surfactant system desorption of linuron from all soils was always greater than in the soil-water system but for atrazine this only occurred at concentrations higher than 50cmc. For the highest Triton X-100 concentration (100cmc), the desorption of the most hydrophobic herbicide (linuron) was increased more than 18-fold with respect to water in soil with an OM content of 10.3% while the atrazine desorption was increased 3-fold. The effect of Triton X-100 on the desorption of both herbicides was very low in soil with a high clay content. The results indicate the potential use of Triton X-100 to facilitate the desorption of these herbicides from soil to the water-surfactant system. They also contribute to better understanding of the interactions of different molecules and surfaces in the complex soil-herbicide-water surfactant system.
研究了在不同有机质(OM)和黏土含量的土壤上吸附的莠去津(1-氯-3-乙氨基-5-异丙氨基-2,4,6-三嗪)和利谷隆[1-甲氧基-1-甲基-3-(3,4-二氯苯基)脲]在水以及不同浓度的非离子表面活性剂吐温X-100存在下的解吸情况。目的是深入了解在表面活性剂增强除草剂从土壤中解吸过程中的土壤特性。在水中、所有吐温X-100溶液中莠去津的吸附和解吸等温线,以及在利谷隆的临界胶束浓度(cmc)的0.75倍和1.50倍的溶液中的吸附和解吸等温线均符合弗伦德利希方程。所有解吸等温线均显示出滞后现象。在吐温X-100溶液中,利谷隆的滞后系数降低,莠去津的滞后系数则升高或降低。这些变化取决于表面活性剂浓度以及土壤的OM和黏土含量。在土壤-水-表面活性剂体系中,所有土壤中利谷隆的解吸量始终大于土壤-水体系中的解吸量,但对于莠去津,仅在浓度高于50cmc时才会出现这种情况。对于最高吐温X-100浓度(100cmc),在OM含量为10.3%的土壤中,疏水性最强的除草剂(利谷隆)相对于水的解吸量增加了18倍以上,而莠去津的解吸量增加了3倍。在黏土含量高的土壤中,吐温X-100对两种除草剂解吸的影响非常小。结果表明吐温X-100在促进这些除草剂从土壤解吸到水-表面活性剂体系方面具有潜在用途。它们还有助于更好地理解复杂的土壤-除草剂-水-表面活性剂体系中不同分子和表面之间的相互作用。