Abstract

제초제 bentazon과 그 대사산물들의 토양흡착 양상을 Freundlich, Langmuir 그리고 linear isotherm을 이용하여 파악하고 기능이 다른 흡착제들과의 흡착특성을 조사하였다. 토양에 대한 bentazon의 <TEX>$K_f$</TEX> = 0.55 L/kg, <TEX>$Q^0$</TEX> = 3.97mg/kg, Kd = 0.18 L/kg 그리고 <TEX>$K_{oc}$</TEX> = 18 L/kg로 나타났다. Deisopropylbentazon을 제외한 다른 대사산물들의 토양 흡착량은 bentazon보다 많았으며 특히 8-hydroxybentazon의 경우 <TEX>$K_f$</TEX> = 316.5 L/kg, <TEX>$Q^0$</TEX> = 3,448 mg/kg, <TEX>$K_d$</TEX> = 29.7 L/kg 그리고 <TEX>$K_{oc}$</TEX> = 2,970 L/kg으로 토양 중에서 대부분이 흡착되는 것으로 나타났다. 여러 기능을 가진 SPE 충진제를 이용하여 bentazon과 그 대사산물들의 흡착양상을 확인한 결과 bentazon, deisopropylbentazon 및 8-hydroxybentazon은 <TEX>$NH_2$</TEX>와 anion exchange phase에 친화성이 큰 것으로 나타났다. N-methylbentazon의 경우 <TEX>$C_{18}$</TEX>에 큰 친화력을 보였으나 normal phase인 silica gel에는 상대적으로 다른 화합물보다 친화력이 낮았다. IBA는 silica gel, COOH 그리고 cation exchange phase에 강한 흡착을 보였으며 상대적으로 <TEX>$NH_2$</TEX> 그리고 anion exchange phase에는 친화력이 낮았다. 2-Aminobenzoic acid의 경우 pH 3.0에서는 COOH, cation exchange phase에 많은 retention을 보였으며 pH 7.0에서는 <TEX>$NH_2$</TEX>, anion exchange phase에 큰 흡착량을 보였다. In order to elucidate the adsorption mechanism of the herbicide, bentazon and its metabolites on soil, their adsorption patterns on soil and six adsorbents were investigated with Freundlich, Langmuir and linear isotherm. Freundlich constants (<TEX>$K_f$</TEX>) and maximum adsorption amount(<TEX>$Q^0$</TEX>) of bentazon on soil was 0.55 and 3.97. Kd and Koc values of it were 0.18 and 18. The all of metabolites used except deisopropylbentazon amounts sorbed on the soil were much higher than bentazon. The most of 8-hydroxybentazon was adsorbed on soil showing <TEX>$K_f$</TEX> = 316.6, <TEX>$Q^0$</TEX> = 3,488, Kd = 29.7 and Koc = 2,970. Bentazon, deisopropylbentazon and 8-hydroxybentazon were shown high affinity to anion exchange regardless of pH and <TEX>$NH_2$</TEX> in low pH range. Reversed phase <TEX>$C_{18}$</TEX> resulted in 100% retention of N-methylbentazon regardless of pH and other metabolites were retained below 40%. The AIBA was strongly adsorbed in silica gel, COOH and cation exchange phase but poor retention was on anion exchange sorbent. 2-Aminobenzoic acid showed an amphipathic nature which had high affinity for COOH and cation exchange phase at pH 7.0 as well as <TEX>$NH_2$</TEX> and anion exchange sorbent at pH 3.0.

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