Novick N J, Alexander M
Appl Environ Microbiol. 1985 Apr;49(4):737-43. doi: 10.1128/aem.49.4.737-743.1985.
Low concentrations of propachlor (2-chloro-N-isopropylacetanilide) and alachlor [2-chloro-2',6'-diethyl-N-(methoxymethyl)acetanilide] were not mineralized, cycloate (S-ethyl-N-ethylthiocyclohexanecarbamate) was slowly or not mineralized, and aniline and cyclohexylamine were readily mineralized in sewage and lake water. Propachlor, alachlor, and cycloate were extensively metabolized, but the products were organic. Little conversion of propachlor and alachlor was evident in sterilized sewage or lake water. The cometabolism of propachlor was essentially linear with time in lake water and was well fit by zero-order kinetics in short periods and by first-order kinetics in longer periods in sewage. The rate of cometabolism in sewage was directly proportional to propachlor concentration at levels from 63 pg/ml to more than 100 ng/ml. Glucose but not aniline increased the yield of products formed during propachlor cometabolism in sewage. No microorganism able to use propachlor as a sole source of carbon and energy was isolated, but bacteria isolated from sewage and lake water metabolized this chemical. During the metabolism of this herbicide by two of the bacteria, none of the carbon was assimilated. Our data indicate that cometabolism of these pesticides takes place at concentrations of synthetic compounds that commonly occur in natural waters.
低浓度的毒草安(2-氯-N-异丙基乙酰苯胺)和甲草胺[2-氯-2',6'-二乙基-N-(甲氧基甲基)乙酰苯胺]未被矿化,环草敌(S-乙基-N-乙基硫代环己烷氨基甲酸酯)被缓慢矿化或未被矿化,而苯胺和环己胺在污水和湖水中易于被矿化。毒草安、甲草胺和环草敌被广泛代谢,但产物为有机物。在经过灭菌处理的污水或湖水中,毒草安和甲草胺的转化不明显。在湖水中,毒草安的共代谢基本随时间呈线性,在短时间内符合零级动力学,在污水中较长时间内符合一级动力学。在污水中,共代谢速率与毒草安浓度在63 pg/ml至超过100 ng/ml的水平上成正比。葡萄糖而非苯胺增加了污水中毒草安共代谢过程中形成的产物产量。未分离出能够将毒草安作为唯一碳源和能源利用的微生物,但从污水和湖水中分离出的细菌能够代谢这种化学物质。在两种细菌对这种除草剂的代谢过程中,没有碳被同化。我们的数据表明,这些农药的共代谢发生在天然水体中常见的合成化合物浓度下。