Bollag J M, Myers C J, Minard R D
Laboratory of Soil Biochemistry, Pennsylvania State University, University Park 16802.
Sci Total Environ. 1992 Aug 12;123-124:205-17. doi: 10.1016/0048-9697(92)90146-j.
There is little doubt that organic matter plays a major role in the binding of pesticides in soil, and that this phenomenon is usually the most important cause for interaction of pesticides in the soil environment. Fulvic or humic acids are the chemicals most commonly involved in the binding interactions. Binding can occur with the original pesticide or a transformation product, the reaction being caused by abiotic agents or biotic agents (microbial or plant enzymes). The reactions or processes involved appear to be the same as those responsible for the formation of humic substances, i.e. for the humification process. Binding of pesticides to organic matter can occur by sorption (Van der Waal's forces, hydrogen bonding, hydrophobic bonding), electrostatic interactions (charge transfer, ion exchange or ligand exchange), covalent bonding or combinations of these reactions. Our investigation focused primarily on the binding of substituted phenols and aromatic amines to humus monomers and humic substances. In model reactions, we demonstrated the formation of covalent linkages between pesticides and humus constituents and fulvic or humic acids in the presence of phenol oxidases or clay minerals. With chlorinated phenols and carboxylic acids, it was possible to isolate and identify cross-coupling products and to elucidate the site and type of binding. The binding of chlorinated phenols to humic substances was determined by using 14C-labelled chemicals and by measuring the uptake of radioactivity by the humic material. These experiments provide a base for explaining the formation of bound residues in certain cases and for assuming the toxic potential of the immobilized pollutants.
毫无疑问,有机物质在土壤中农药的结合过程中起着主要作用,而且这种现象通常是土壤环境中农药相互作用的最重要原因。富里酸或腐殖酸是最常参与结合相互作用的化学物质。结合可以发生在原始农药或转化产物上,反应由非生物因素或生物因素(微生物或植物酶)引起。所涉及的反应或过程似乎与腐殖物质形成过程中的相同,即与腐殖化过程相同。农药与有机物质的结合可以通过吸附(范德华力、氢键、疏水键)、静电相互作用(电荷转移、离子交换或配体交换)、共价键或这些反应的组合来实现。我们的研究主要集中在取代酚和芳香胺与腐殖质单体及腐殖物质的结合上。在模型反应中,我们证明了在酚氧化酶或粘土矿物存在的情况下,农药与腐殖质成分以及富里酸或腐殖酸之间形成了共价键。对于氯酚和羧酸,可以分离并鉴定交叉偶联产物,并阐明结合的位点和类型。通过使用14C标记的化学物质并测量腐殖质材料对放射性的吸收,确定了氯酚与腐殖物质的结合。这些实验为解释某些情况下结合残留的形成以及推测固定污染物的潜在毒性提供了依据。