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Adsorption of the insecticidal protein of Bacillus thuringiensis on montmorillonite, kaolinite, silica, goethite and Red soil

机译:苏云金芽孢杆菌的杀虫蛋白在蒙脱石,高岭石,硅石,针铁矿和红壤上的吸附

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摘要

The adsorption and desorption of the insecticidal protein (toxin) of Bacillus thuringiensis strain WG-001 on montmorillonite, Red soil, goethite, kaolinite and silica were studied. The adsorption isotherms of toxin in sodium carbonate buffer (pH 9) followed Langmuir equation (R~2 >0.97) and the curves belonged to L type. The amounts of toxin adsorbed were in the order: montmorillonite > Red soil > goethite > kaolinite > silica. At pH from 6 to 8 (phosphate buffer), the maximum adsorption of toxin on Red soil, kaolinite and goethite occurred at pH 6, while that on montmorillonite and silica were observed at pH 7. In the range of pH from 9 to 11 (carbonate buffer), the toxin adsorbed decreased with increasing pH. The adsorption of toxin on montmorillonite and Red soil reached equilibrium within 0.5 h, and in 1-3 h for goethite, kaolinite and silica systems. The adsorption was not significantly affected by the temperature between 10℃ and 50℃. Both free and adsorbed toxin were toxic to the larvae of Heliothis armigera. The LC_(50) value of adsorbed toxin was smaller than that of free toxin. The desorption of adsorbed toxin in water ranged from 24.7% to 40.5% and were from 16.3% to 38.8% in carbonate buffer.
机译:研究了苏云金芽孢杆菌WG-001菌株的杀虫蛋白(毒素)在蒙脱土,红壤,针铁矿,高岭石和二氧化硅上的吸附和解吸。碳酸钠缓冲液(pH 9)中毒素的吸附等温线符合Langmuir方程(R〜2> 0.97),曲线属于L型。吸附的毒素的顺序为:蒙脱土>红壤>针铁矿>高岭土>二氧化硅。在6到8的pH(磷酸盐缓冲液)下,在pH值为6时,红壤,高岭石和针铁矿上的毒素最大吸附发生在pH值为7的情况下。在9到11(碳酸盐缓冲液),吸附的毒素随pH值的增加而降低。毒素在蒙脱土和红壤上的吸附在0.5 h内达到平衡,针铁矿,高岭石和二氧化硅体系在1-3 h内达到平衡。 10℃至50℃之间的温度对吸附没有明显的影响。游离毒素和吸附毒素均对棉铃虫的幼虫有毒。吸附毒素的LC_(50)值小于游离毒素的LC_(50)值。水中吸附的毒素在碳酸盐缓冲液中的解吸率为24.7%至40.5%,为16.3%至38.8%。

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