Position: Home > Articles > Adsorption and Its Mechanisms of Novel Insecticide HNPC-A9908 on Clay Minerals and Humic Acids
Journal of Agro-Environment Science
2006,25
(01)
211-218
黏土矿物和腐植酸对新农药硫肟醚的吸附及其机理研究
作 者:
欧晓明;罗玲;王晓光;樊德方
单 位:
湖南化工研究院国家南方农药创制中心湖南基地;浙江大学农药环境毒理研究所;长沙环保职业技术学院
关键词:
肟醚类农药;硫肟醚;黏土矿物;腐植酸;吸附与机理
摘 要:
硫肟醚[O-(3-苯氧苄基)-2-甲硫基-1-(4-氯苯基)丙基酮肟醚]是国家南方农药创制中心湖南基地研制成功的首个具有我国自主知识产权的一种新型杀虫剂。为了深入认识硫肟醚在土壤中的归宿,在室内条件下采用振荡平衡法和红外光谱法(IR)对硫肟醚在黏土矿物和腐植酸上的吸附及其机理进行了研究。结果表明,硫肟醚在黏土矿物钙-蒙脱石(Ca-Clay)上的吸附等温线属于S型,而在腐植酸(HAs)上的等温线属于L型,说明硫肟醚在黏土矿物上的吸附量要大于腐植酸。硫肟醚在黏土矿物和腐植酸上的吸附等温线符合Freundlich方程,在相同试验条件下,黏土矿物对硫肟醚的吸附系数KF值为腐植酸的5.45倍。通过自载膜法研究了黏土矿物与硫肟醚作用物的IR谱图,结果发现黏土矿物与硫肟醚作用物的IR图谱中不仅出现了明显的硫肟醚吸收峰,而且黏土矿物与硫肟醚作用后其主要特征吸收峰的位置、形态和强度均发生了变化,由此推测它们之间产生了氢键键合和配位键结合作用。同样地,腐植酸与硫肟醚作用物的IR谱图中也出现了类似的结果。腐植酸与黏土矿物作用后会明显降低对硫肟醚的吸附,但腐植酸与黏土矿物不同比例的复合物对硫肟醚的吸附不同,其中以50∶50的复合体对硫肟醚的吸附量减少最明显。黏土矿物与HAs在不同时间形成的复合体对硫肟醚的吸附作用是不同的。随着钙-蒙脱石与HAs作用时间的延长,其复合体对硫肟醚的吸附量会逐渐下降,钙-蒙脱石与HAs作用时间进一步增加,复合体对硫肟醚的吸附量将开始上升,21d时达到最大吸附值,此后随作用时间的继续延长,吸附量会有所下降,28d后其吸附量接近于初始值。
译 名:
Adsorption and Its Mechanisms of Novel Insecticide HNPC-A9908 on Clay Minerals and Humic Acids
作 者:
OU Xiao-ming1, LUO Ling2, WANG Xiao-guang1, FAN De-fang3 (1. Hunan Branch of National Pesticide R&D South Center, Hunan Research Institute of Chemical Industry, Changsha 410007, China; 2. Changsha Environmental Protection College, Changsha 410004, China; 3. Institute of Pesticide & Environmental Toxicology, Zhejiang University, Hangzhou 310029, China)
关键词:
oxime insecticide; HNPC-A9908; clay mineral; humic acid; adsorption and mechanism
摘 要:
HNPC-A9908 [O- (3-phenoxybenzyl)- 2-methylthio- 1-(4-chlorophenyl) propyl ketone oxime] is a novel oxime insecticide that is discovered and developed by Hunan Branch of the National Pesticide R & D South Center. It can be used to control effectively various pest insects such as imported cabbageworm Pieris rapae, rice leafhopper Nephotettix cincticeps, oriental armyworm Mythimna separata, tea tussock moth Euproctis pseudoconspersa, tea geometer Ectropis oblique, tea green leafhopper Empoasca spp, etc on vegetable, rice, tea and other crops. Adsorption and its mechanisms of HNPC-A9908 on clay, humic acid and their complexes in the laboratory using batch equilibrium. Adsorption isotherm of HNPC-A9908 on the Ca-saturated montmorillonite (Ca-Clay) was S-type, the adsorption active site of HNPC-A9908 on the clay surface decreased gradually with the concentration increasing of HNPC-A9908, and finally reached a plateau level. However, adsorption of HNPC-A9908 on humic acid exhibited L-type isotherm, suggesting that the humic acids have a great affinity to HNPC-A9908. Adsorption of HNPC-A9908 on clay and humic acids fitted Freundlich equation very well, and under the same conditions, adsorption coefficient KF of HNPC-A9908 on Ca-Clay was 5.45 times of that on humic acids. The IR chromatograph of Ca-Clay and HNPC-A9908 complexes showed that there existed some absorbance peaks of HNPC-A9908, and the major characteristic of absorbance peaks, such as sites, shapes and intensity, also changed, demonstrating that hydrogen bonding and coordination formed between HNPC-A9908 and Ca-Clay. Meanwhile, there also appeared the similar results in the humic acids and HNPC-A9908 complexes. The binary complexes of Ca-Clay and humic acids could reduce obviously the adsorption amount of HNPC-A9908 on Ca-Clay and humic acids, but adsorption amount varied with ratios of Ca-Clay and humic acids, the lowest adsorption of HNPC-A9908 appeared at 50∶50 complex of Ca-Clay and humic acids. There appeared a different adsorption of HNPC-A9908 on the complexes that formed at different times. Adsorption amount of HNPC-A9908 on the complexes decreased gradually with prolonging action time of Ca-Clay and humic acids. When the action time of the complexes went on, the adsorption amount began to increase and reached the maximum at 21 d, after that, it decreased, close to the initial level at 28 d.