潮上盐沼地点反复空中施用灭蚊剂后水和沉积物中灭蚊脲(二米灵®)浓度的动态变化

P.A. Cunningham , L.E. Myers
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引用次数: 12

摘要

进行了一项实地研究,以监测从潮上蚊虫繁殖泻湖收集的水和沉积物中双氟苯脲(DFB)和降解产物4-氯苯脲(CPU)的变化。在现场进行了三次应用0.4%的砂粒,然后三次应用25%的可湿性粉末配方。在不同的应用中,水中DFB和CPU浓度的动态变化存在显著差异。在一些应用中,水中DFB浓度的对数作为时间函数的非线性也很明显。在这种情况下,半衰期参数不能表征过程的动力学,其值值得怀疑。在6次施用中,有4次明显降低了水中DFB浓度。然而,没有明显证据表明沉积物中DFB浓度下降,而沉积物似乎是DFB吸附的主要场所。每种分析物的水浓度(DFB, CPU)与同一分析物的沉积物浓度呈负相关,表明两种分析物在水/沉积物界面上发生交换。水体和沉积物中DFB与CPU均呈显著正相关。如果假设DFB和CPU浓度的变化主要是由于前者对后者的退化,那么这些相关性发现是违反直觉的。虽然在施用后7天内,潮上泻湖水体中的DFB浓度往往保持在0.4 μg升- 1以上,但如果DFB通过径流或潮上地区的洪水进入邻近河口,这种毒性浓度似乎不太可能影响这些水域的浮游甲壳类幼虫。然而,水和沉积物中持续的DFB浓度(~ 100 μgkg - 1)可能对沼泽甲壳类动物(如Uca)的有害种群有害。
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Dynamics of diflubenzuron (dimilin®) concentrations in water and sediment of a supratidal saltmarsh site following repetitive aerial applications for mosquito control

A field study was conducted to monitor changes in diflubenzuron (DFB) and a degradation product, 4-chlorophenylurea (CPU) in water and sediment collected from a supratidal mosquito breeding lagoon. Three applications of a 0·4% sand granule followed by three applications of a 25% wettable powder formulation were made to the site. Substantial differences in the dynamics of both DFB and CPU concentrations in water were noted among applications. Non-linearity of the logarithm of DFB concentrations in water as a function of time was also evident in some applications. In such cases, the half-life parameter does not characterise the dynamics of the process and is of questionable value.

For four of the six applications, there was strong evidence of a decrease in DFB concentration in water. However, there was not significant evidence of a decrease in DFB concentrations in sediment, which appeared to be a major site for DFB adsorption. Water concentrations for each analyte (DFB, CPU) were negatively correlated with sediment concentrations for the same analyte, suggesting that an exchange of both analytes occurs across the water/sedimetn interface. Also, positive correlations were noted between DFB and CPU in both water and sediment. These correlation findings are counter-intuitive, if it is assumed that changes in DFB and CPU concentrations are mainly due to degradation of the former to the latter.

While DFB concentrations in the supratidal lagoon water tended to remain above 0·4 μg litre−1 for 7 days post application, it seems unlikely that this toxic concentration would affect planktonic larval crustaceans in adjacent estuaries if DFB entered these waters via runoff or by flooding of supratidal areas. The persistent DFB concentrations in the water and sediment (∼100 μgkg−1), however, could be detrimental to detrialfeeding populations of marsh crustaceans (e.g. Uca).

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