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The effect of the runoff size on the pesticide concentration in runoff water and in FOCUS streams simulated by PRZM and TOXSWA

机译:径流大小对PRZM和TOXSWA模拟的径流水和FOCUS流中农药浓度的影响

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Within the European Union the exposure of aquatic organisms to pesticides is assessed by simulations with the so-called FOCUS Surface Water Scenarios. Runoff plays an important role in these scenarios. As little is known about the effect of runoff size on the exposure, we investigated the effect of runoff size on the concentration in the runoff water and in streams simulated with the PRZM and TOXSWA models for two FOCUS runoff scenarios. For weakly sorbing pesticides (K_(F,oc) < 100 L kg~(− 1)) the pesticide concentration in the runoff water decreased exponentially with increasing daily runoff size. The runoff size hardly affected the pesticide concentration in the runoff water of strongly sorbing pesticides (K_(F,oc) ≥ 1000 L kg~(− 1)). For weakly sorbing pesticides the concentration in the FOCUS stream reached a maximum at runoff sizes of about 0.3 to 1 mm. The concentration increased rapidly when the runoff size increased from 0 to 0.1 mm and gradually decreased when runoff exceeded 1 mm. For strongly sorbing pesticides the occurrence of the maximum concentration in the stream is clearly less pronounced and lies approximately between 1 and 20 mm runoff. So, this work indicates that preventing small runoff events (e.g. by vegetated buffer strips) reduces exposure concentrations strongly for weakly sorbing pesticides. A simple metamodel was developed for the ratio between the concentrations in the stream and in the runoff water. This model predicted the ratios simulated by TOXSWA very well and it demonstrated that (in addition to runoff size and concentration in runoff) the size of the pesticide-free base flow and pesticide treatment ratio of the catchment determine the stream concentration to a large extent.
机译:在欧盟内部,通过所谓的FOCUS地表水情景模拟来评估水生生物对农药的暴露。在这些情况下,径流起着重要作用。对于径流大小对暴露的影响知之甚少,我们研究了径流大小对两种FOCUS径流情景下PRZM和TOXSWA模型模拟的径流水和溪流中浓度的影响。对于弱吸收农药(K_(F,oc)<100 L kg〜(-1)),径流水中的农药浓度随日径流量的增加而呈指数下降。径流大小几乎不会影响强吸附农药(K_(F,oc)≥1000 L kg〜(-1))径流水中的农药浓度。对于吸附力较弱的农药,在径流大小约为0.3至1毫米时,FOCUS流中的浓度达到最大值。当径流大小从0增加到0.1mm时,浓度迅速增加,而当径流超过1mm时浓度逐渐减小。对于强吸附性农药,流中最大浓度的出现明显不太明显,大约在1至20毫米径流之间。因此,这项工作表明防止小径流事件(例如通过植被缓冲带)会大大降低弱吸收农药的暴露浓度。针对溪流和径流水中的浓度之比,开发了一个简单的元模型。该模型很好地预测了TOXSWA模拟的比率,并且证明了(除径流大小和径流浓度外)无农药基流的大小和集水区的农药处理比率在很大程度上决定了水流浓度。

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