INRA, AgroParisTech, UMR 1091 EGC, Thiverval-Grignon, France.
Pest Manag Sci. 2011 Apr;67(4):397-407. doi: 10.1002/ps.2077. Epub 2011 Jan 6.
Mobility of pesticides in soils is often evaluated and characterised in the surface soil layers rather than at different depths where soil characteristics such as soil organic matter, microbial biomass or clay contents can strongly change pesticide behaviour. The objective of this work was to characterise the reactivity of the herbicide metribuzin in three main soil horizons found in the 0-80 cm profile of an alluvial soil of southern Norway under dynamic transport conditions.
A laboratory infiltrometer was used to perform percolation experiments in soil cores sampled in the three horizons Ap, Bw and Bw/C, at a fixed matric potential of -10 cm, thus preventing pores of equivalent radii higher than 0.015 cm from contributing to water flow. The physical equilibrium transport model correctly described the transport of water tracer (bromide). The distribution coefficient K(d) values were estimated to be 0.29, 0.17 ± 0.02 and 0.15 ± 0.00 L kg(-1) for horizons Ap, Bw and Bw/C respectively, in close agreement with batch sorption data. Degradation was found only for the surface horizon with a short half-life of about 5 days, in disagreement with longer half-lives found in batch and field degradation data.
For all horizons, a kinetic sorption model was needed for better description of metribuzin leaching. Chemical non-equilibrium was greatest in the Bw horizon and lowest in the Bw/C horizon. Overall, metribuzin exhibited a greater mobility in the deeper horizons. The risk of metribuzin transfer to groundwater in such alluvial soils should therefore be considered.
土壤中农药的迁移性通常在表层土壤中进行评估和描述,而不是在不同深度进行评估,因为土壤特性(如土壤有机质、微生物生物量或粘粒含量)会强烈改变农药的行为。本研究的目的是在挪威南部冲积土 0-80cm 剖面的三个主要土壤层中,在动态传输条件下,对除草剂嗪草酮的反应性进行特征描述。
使用实验室渗滤仪在 Ap、Bw 和 Bw/C 三个土壤层中采集的土壤芯进行渗滤实验,在固定基质势-10cm 的条件下进行,从而防止等效半径大于 0.015cm 的孔隙对水流产生贡献。物理平衡传输模型正确描述了水示踪剂(溴化物)的传输。分配系数 K(d)值分别为 0.29、0.17±0.02 和 0.15±0.00Lkg(-1),与批量吸附数据非常吻合。仅在表层发现了降解,半衰期约为 5 天,与批量和田间降解数据中发现的较长半衰期不一致。
对于所有土壤层,需要使用动力学吸附模型来更好地描述嗪草酮的淋溶。Bw 层的化学非平衡最大,Bw/C 层的化学非平衡最小。总体而言,嗪草酮在较深的土壤层中具有更大的迁移性。因此,应考虑此类冲积土壤中嗪草酮向地下水转移的风险。