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Potential contributions of smectite clays and organic matter to pesticide retention in soils.

机译:蒙脱石粘土和有机物对农药在土壤中滞留的潜在贡献。

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Soil organic matter (SOM) is often considered the dominant sorptive phase for organic contaminants and pesticides in soil-water systems. This is evidenced by the widespread use of organic-matter-normalized sorption coefficients (K(OM)) to predict soil-water distribution of pesticides, an approach that ignores the potential contribution of soil minerals to sorption. To gain additional perspective on the potential contributions of clays and SOM to pesticide retention in soils, we measured sorption of seven pesticides by a K-saturated reference smectite clay (SWy-2) and SOM (represented by a muck soil). In addition, we measured the adsorption of atrazine by five different K-saturated smectites and Ca-saturated SWy-2. On a unit mass basis, the K-SWy-2 clay was a more effective sorbent than SOM for 4,6-dinitro-o-cresol (DNOC), dichlobenil, and carbaryl of the seven pesticides evaluated, of which, DNOC was sorbed to the greatest extent. Atrazine was sorbed to a similar extent by K-SWy-2 and SOM. Parathion, diuron, and biphenyl were sorbed to a greater extent by SOM than by K-SWy-2. Atrazine was adsorbed by Ca-SWy-2 to a much lesser extent than by K-SWy-2. This appears to be related to the larger hydration sphere of Ca(2+) (compared to that of K(+)) which shrinks the effective size of the adsorption domains between exchangeable cations, and which expands the clay layers beyond the apparently optimal spacing of approximately 12.2 A for sorption of aromatic pesticide structures. Although a simple relation between atrazine adsorption by different K-smectites and charge properties of clay was not observed, the highest charge clay was the least effective sorbent; a higher charge density would result in a loss of adsorption domains. These results indicate that for certain pesticides, expandable soil clays have the potential to be an equal or dominant sorptive phase when compared to SOM for pesticide retention in soil.
机译:土壤有机质(SOM)通常被认为是土壤-水系统中有机污染物和农药的主要吸附相。这可以通过有机物归一化吸附系数(K(OM))广泛用于预测农药在土壤中水的分布来证明,该方法忽略了土壤矿物对吸附的潜在贡献。为了进一步了解粘土和SOM对土壤中农药残留的潜在贡献,我们测量了K饱和参比蒙脱石粘土(SWy-2)和SOM(以泥土代表)对7种农药的吸附。此外,我们测量了5种不同的K饱和蒙脱石和Ca饱和SWy-2对阿特拉津的吸附。以单位质量计,K-SWy-2黏土对7种评价农药中的4,6-二硝基邻甲酚(DNOC),二氯苯腈和西维因的吸附剂比SOM更有效,其中DNOC被吸附在最大程度上。阿特拉津被K-SWy-2和SOM吸附的程度相似。与K-SWy-2相比,SOM吸附对硫磷,二ur和联苯的程度更大。 r去津被Ca-SWy-2吸附的程度比K-SWy-2少得多。这似乎与Ca(2+)的较大水化球(与K(+)的水化球)有关,后者缩小了可交换阳离子之间的吸附域的有效尺寸,并使粘土层扩展到了明显最佳的间距之外大约12.2 A的吸附能力可吸收芳香农药结构。尽管未观察到不同K-蒙脱石对at去津的吸附与粘土的电荷性质之间的简单关系,但电荷最高的粘土是最不有效的吸附剂。较高的电荷密度将导致吸附域的损失。这些结果表明,对于某些农药,与将SOM保留在土壤中的SOM相比,膨胀性粘土有可能成为相等或占优势的吸附相。

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