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Aerial short-range dispersion of volatilized pesticides from an area source

机译:从区域源空中挥发农药的短程空中扩散

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Owing to legal provisions, pesticides have to be applied in such a way that there is no unacceptable influence on human health and the environment at nearby non-target areas. In order to quantify their concentration over and downwind of agricultural target plots of 0.5-1 ha, covered by winter wheat and winter barely, the pesticides lindane, parathion and pirimicarb were applied. Over these plots the post-application volatilization rates of the pesticides were estimated indirectly from vertical concentration, wind and temperature profile measurements using the aerodynamic gradient technique. Philip's advection model was applied to take non-favourable fetch conditions into account. In addition, at a height of 1.6 in downwind of the area source, measurements of the horizontal concentration profile were made up to a distance of about 250 m at roughly 50-m intervals. The monitoring started immediately after spraying in the morning and continued for about 8-10 h, thus providing a worst-case situation because volatilization, and therefore pesticide concentration in the atmospheric surface layer, is then strongest. The concentration of the airborne pesticides over the downwind non-target area was also calculated by Philip's advection model. By using the Nash-Sutcliffe relative-difference measure between observed and calculated concentrations, a goodness-of-fit of 0.97 was obtained over the downwind non-target area, indicating that the Philip model is well suited for dispersion estimates in the near-field range.
机译:根据法律规定,必须以不对附近非目标区域的人类健康和环境造成不可接受的影响的方式使用农药。为了定量测定0.5-1公顷的农业目标地块的上,下游风向的浓度,这些目标地块被冬小麦和几乎没有冬季覆盖,使用了林丹,对硫磷和吡虫威杀虫剂。在这些地块上,使用空气动力学梯度技术通过垂直浓度,风和温度曲线测量值间接估算了农药施用后的挥发速率。菲利普的对流模型用于考虑不利的取货条件。另外,在区域源顺风向的高度为1.6处,水平浓度分布的测量值以大约50-m的间隔进行到大约250m的距离。监测是在早上喷洒后立即开始的,并持续约8-10小时,因此是最坏的情况,因为挥发和因此在大气表层的农药浓度最强。还通过Philip的对流模型计算了顺风非目标区域上的空气传播农药浓度。通过使用纳什-苏特克利夫观测值和计算值之间的相对差度量,在下风向非目标区域获得了0.97的拟合优度,表明Philip模型非常适合于近场中的色散估计范围。

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