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LEACHING AND DEGRADATION OF PESTICIDES IN GROUNDWATER LAYERS

机译:地下水中农药的浸出和降解

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摘要

To date, most of the published data on pesticides and soil describe the fate of environmental contaminants in the upper soil layers, where low transportation, high adsorption and high microbial degradation occur. In contrast, few data are available for groundwater layers (to a depth of 5 m) with filtration media such as sand or stony layers. Laboratory testing systems were developed that allow examinations to be carried out under conditions that are close to natural. These include original sands and stones from the relevant groundwater filtration areas, original water from the same areas, and measurement of the velocity of water migrations. The temperature and pH were determined and exact analyses of the sand quality and particle size were made prior to the experiments. To produce accurate data on leaching and adsorption, and to identify the degradation products more easily, ~(14)C labelled pesticides were applied. To determine the column characteristics, tritium labelled water was used. The following 12 pesticides were investigated: the carbamate insecticide, carbofuran; chlorinated hydrocarbons, lindane, DDT and DDE; phosphoric acid esters, chlorpyrifos, diazinon, malathion and parathion; phenylurea herbicides, diuron and monolinuron; the triazine herbicide, terbutylazine; and the novel chloronicotinyl insecticide, imidacloprid. Although the recovery data of the individual pesticides were similar in the eluates of the two different sand types, in most cases the elution curves differed significantly. The different degradation rates and procedures for the same pesticide were clearly shown by the significantly different concentration values. Concerning elution and degradation, the behaviour of the chemicals differed, even if they belonged to the same class of bioactive compound. Furthermore, the behaviour of the same chemical differed in different types of sand. Because of the low transportation velocity, and the subsequent long retention times of the pesticides in the sand media, microbial degradation (metabolisms) can also take place.
机译:迄今为止,大多数有关农药和土壤的公开数据都描述了土壤上层环境的命运,在土壤上层发生低迁移,高吸附和高微生物降解。相比之下,很少有过滤层(如沙层或石质层)的地下水层(深度为5 m)的数据。开发了实验室测试系统,可以在接近自然的条件下进行检查。这些包括来自相关地下水过滤区域的原始沙子和石头,来自相同区域的原始水以及水迁移速度的测量。确定温度和pH,并在实验前对砂的质量和粒度进行精确分析。为了产生关于浸出和吸附的准确数据,并更容易地识别降解产物,使用了〜(14)C标记的农药。为了确定色谱柱特性,使用了labeled标记的水。调查了以下12种农药:氨基甲酸酯类杀虫剂,呋喃丹;氯代烃,林丹,滴滴涕和滴滴涕;磷酸酯,毒死rif,二嗪农,马拉硫磷和对硫磷;苯脲除草剂,敌草隆和单亚麻嘧啶;三嗪除草剂叔丁嗪;以及新型氯烟碱杀虫剂吡虫啉。尽管两种不同类型沙子的洗脱液中单个农药的回收率数据相似,但在大多数情况下,洗脱曲线差异很大。明显不同的浓度值清楚地表明了同一农药的不同降解速率和程序。关于洗脱和降解,即使它们属于同一类生物活性化合物,其化学性质也有所不同。此外,相同化学物质的行为在不同类型的沙子中也有所不同。由于较低的运输速度,以及随后农药在沙质介质中的较长保留时间,也可能发生微生物降解(代谢)。

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