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根际中两种有机磷杀虫剂的加速矿化作用

Accelerated mineralization of two organophosphate insecticides in the rhizosphere.

作者信息

Hsu T S, Bartha R

出版信息

Appl Environ Microbiol. 1979 Jan;37(1):36-41. doi: 10.1128/aem.37.1.36-41.1979.

Abstract

Numerous xenobiotic compounds, including the organophosphate insecticides O, O-diethyl-O-(2-isopropyl-6-methyl-4-pyrimidinyl) phosphorothioate (diazinon) and O, O-diethyl-O-p-nitrophenyl phosphorothioate (parathion), appear to be degraded in the soil environment by an initial cometabolic attack. Comparing the mineralization rates of radiolabeled diazinon and parathion in root-free and in rhizosphere soil, we tested our hypothesis that, because of the presence of root exudates, the rhizosphere is an especially favorable environment for such co-metabolic transformations. The insecticides were added individually at 5 mug/g to sealed flasks containing either soil permeated by the root system of a bush bean plant or identical soil without roots. Periodically, the flask atmospheres were flushed through traps and the evolved (14)CO(2) was quantitated. Bush bean plant roots without associated rhizosphere microorganisms failed to produce a significant amount of (14)CO(2). During 1 month of incubation, rhizosphere flasks mineralized 12.9 and 17.9% of the added diazinon and parathion radiocarbon, respectively, compared to 5.0 and 7.8% by the soil without roots. The mineralization of parathion but not of diazinon was stimulated in a similar manner when soil without roots was repeatedly irrigated with a root exudate produced in aseptic solution culture. Viable counts of microorganisms on soil extract agar were not significantly altered by root permeation or by root exudate treatment of the soil, leaving population selection and/or enhanced cometabolic activity as the most plausible interpretations for the observed stimulatory effects. Rhizosphere interactions may substantially shorten the predicted half-lives of some xenobiotic compounds in soil.

摘要

许多外源性化合物,包括有机磷酸酯类杀虫剂O,O-二乙基-O-(2-异丙基-6-甲基-4-嘧啶基)硫代磷酸酯(二嗪农)和O,O-二乙基-O-对硝基苯基硫代磷酸酯(对硫磷),似乎在土壤环境中首先通过共代谢攻击而降解。通过比较无根系土壤和根际土壤中放射性标记的二嗪农和对硫磷的矿化率,我们验证了我们的假设,即由于根系分泌物的存在,根际是这种共代谢转化特别有利的环境。将杀虫剂分别以5μg/g的量添加到密封的烧瓶中,烧瓶中装有菜豆植物根系渗透的土壤或相同的无根土壤。定期通过捕集器冲洗烧瓶中的空气,并对释放出的(14)CO(2)进行定量。没有相关根际微生物的菜豆植物根系未能产生大量的(14)CO(2)。在1个月的培养期内,根际烧瓶中添加的二嗪农和对硫磷放射性碳分别矿化了12.9%和17.9%,而无根土壤中的矿化率分别为5.0%和7.8%。当用无菌溶液培养产生的根系分泌物反复灌溉无根土壤时,对硫磷的矿化(但二嗪农的矿化没有)以类似的方式受到刺激。土壤提取物琼脂上微生物的活菌计数没有因根系渗透或土壤的根系分泌物处理而显著改变,因此种群选择和/或增强的共代谢活性是观察到的刺激作用最合理的解释。根际相互作用可能会大大缩短一些外源性化合物在土壤中的预测半衰期。

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