토양내 제초제의 흡착·탈착 특성

The Adsorption and Desorption of Herbicides in Soils

  • Ra, Deog-Gwan (Department of Environmental Engineering, Sunchon National University) ;
  • Park, Sang-Sook (Department of Environmental Engineering, Sunchon National University) ;
  • Jung, Jae-Sung (Department of Environmental Engineering, Sunchon National University) ;
  • Kim, Young-Kyu (College of Engineering, Chonbuk National University) ;
  • O, Tae-Sun (Green Environmental Co.)
  • 투고 : 2000.01.21
  • 심사 : 2000.03.17
  • 발행 : 2000.06.30

초록

제초제로 사용되는 napropamide와 pendimethalin의 토양내 흡착 탈착특성을 파악하기 위하여 진탕시간, 유기물함량, pH, 온도 등을 변화시키면서 실험을 수행하였다. Sandy loam, silty clay, loam 토양에 대하여 napropamide 및 pendimethalin이 흡착 탈착 평형에 도달되기 위한 진탕시간은 각각 12시간 및 6시간으로 나타났다. 평형흡착 탈착에 도달되었을 때 각 토양에 대한 napropamide의 흡착율 및 탈착율은 각각 23.35%, 31.57%, 25.95% 및 18.42%, 13.42%, 15.89%, pendimethalin은 각각 59.61%, 77.26%, 64.02% 및 3.23%, 2.93%, 3.07%이었다. 등온흡착은 Langmuir식보다는 Freundlich식에 적합하였다. 유기물함량이 2.0% 이상에서의 흡착은 유기물의 영향을 받고, 그 이하에서는 점토의 영향을 받고 있음을 알 수 있었다. 유기물함량 0.95~7.45(%)의 범위에서 흡착계수($K_{fa}$) 및 탈착 계수($K_{fd}$)는 napropamide의 경우 1.17~2.50 및 5.33~34.06, pendimethalin은 4.74~16.08 및 24.25~134.00로 나타났다. 따라서 유기물은 농약과 흡착친화력이 높기 때문에 유기물함량이 증가하면 흡착율은 증가하고, 탈착율은 감소하는 경향을 나타내었다. Napropamide와 pendimethalin은 비이온성 농약이기 때문에 pH 변화로 인한 흡착 탈착경향은 거의 변화가 없는 것으로 나타났다. 토양의 온도 변화에 따른 제초제의 흡착율은 온도가 낮을수록 증가하는 경향을 나타냈으며, 탈착율은 온도가 높을수록 증가하는 경향을 나타냈다. 이것은 실험에 사용된 제초제가 낮은 온도에서는 용해도가 낮지만, 높은 온도에서 용해도가 높기 때문이다.

The adsorption and desorption of herbicides such as napropamide and pendimethalin was studied in three kinds of soil. sandy loam. silty clay and loam. The results of batch tests performed with various shaking time, pH, organic matter content and temperature in soil were summarized as follows. The shaking times reached to the equilibrium of the adsorption and desorption for napropamide and pendimethalin in soil were 12 and 6 hours. respectively. For each soil. the adsorption rates of napropamide were 23.35%. 31.57% and 25.95%, the desorption rates of them were 18.42%, 13.42% and 15.89%, respectively. And the adsorption rates of pendimethalin were 59.61%, 77.26% and 64.02%, and the desorption rates of them were 3.23%, 2.93% and 3.07%, respectively. The adsorption isotherms with the Freundlich equation showed better consistency than those with the Langmuir one. The adsorption was affected by the organic matter content when it exceed 2.0%. But if the organic matter content is below 2.0%, it was affected by the clay content. When the organic matter content is 0.95~7.45%, the adsorption coefficients ($K_{fa}$) of napropamide and pendimethalin were 1.17~2.50 and 4.74~16.08 and the desorption coefficients($K_{fd}$) of them were 5.33~34.06 and 24.25~134.00, respectively. Because of the physical adsorption between herbicide molecules and soil surface, little effect of pH variation of soils was appeared for the adsorption and desorption. Because of the solubility of herbicide is related to the temperature, the adsorption rate was decreased and the desorption rate was increased with the temperature increase, respectively.

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