首页> 外文会议>NATO Advanced Research Workshop on Viable Methods of Soil and Water Pollution Monitoring, Protection Remdeiation >ECOREMEDIATION. COOPERATION BETWEEN PLANTS AND SOIL MICROORGANISMS, MOLECULAR ASPECTS AND LIMITS
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ECOREMEDIATION. COOPERATION BETWEEN PLANTS AND SOIL MICROORGANISMS, MOLECULAR ASPECTS AND LIMITS

机译:生态化。植物与土壤微生物之间的合作,分子方面和限制

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In terrestrial ecosystems, higher plants are organized in two quite different spatial parts: a) a photosynthetjc compartment, developed in the atmosphere, under light, and b) a soil compartment, specialized in the absorption of water and mineral salts, in the dark. An intense flux of water, of mineral salts and of organic compounds passes from the soil to the leaves. Small non-charged organic molecules with a medium lipophilicity can move passively in the transpiration stream, from soil water to the transpirating leaves. The composition of the soil solution is regulated by adsorption on the clay-humus complex and by exchanges with the microbial biomass. In the course of evolution, co-occuring microbes and plants have both developed, or maintained antitoxic properties allowing them to transform a large range of molecules, which are not among the group of essential compounds needed for microbial nor plant life. These antitoxic biochemical capabilities are generally not induced by the presence of a toxic property, but often only by foreign, unknown molecules. The case of phytoalexins seems to be an exception to this rule. Organic molecules reaching the soil are first submitted to microbial transformation, and plants absorb a mixture of molecules, of limited log P, either unchanged or partly transformed by microbes. During plant necrosis, the molecules which had been previously absorbed, and which are partly transformed by plant enzymes, are released into the soil and new transformations occur at this level, finally giving a complete mineralization. These mechanisms are illustrated by the case of two pesticides, atrazine and fipronil.
机译:在地面生态系统中,高植物在两个相当不同的空间部件中组织:a)在大气中,在浅色和b)下,在黑暗中,在大气中发育的光学池,在黑暗中,专门从事水和矿物盐。矿物盐和有机化合物的强烈助焊剂从土壤中通过土壤。具有中等亲脂性的小型非充电有机分子可以在蒸腾物流中被动地移动,从土壤水到递送叶片。土壤溶液的组成通过对粘土腐殖质复合物的吸附和与微生物生物量的交换来调节。在进化过程中,共同发生微生物和植物具有显影,或维持抗毒性,允许它们转化大量分子,这些分子不是微生物或植物寿命所需的必需化合物组中。这些抗毒性生物化学能力通常不受毒性特性的存在,但通常仅由外国未知的分子诱导。 Phytoalexins的情况似乎是这条规则的例外。达到土壤的有机分子首先提交到微生物转化,并且植物吸收有限的LOG P的分子混合物,无论是不变的还是由微生物转化的。在植物坏死期间,先前被植物酶部分被吸收的分子释放到土壤中,在该水平上发生新的转化,最终出现完全的矿化。这些机制通过两种农药,尿嘧啶和氟罗尼尔的情况说明。

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