首页> 外文期刊>Archives of Environmental Contamination and Toxicology >Soil dissipation of diuron, chlorotoluron, simazine, propyzamide, and diflufenican herbicides after repeated applications in fruit tree orchards.
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Soil dissipation of diuron, chlorotoluron, simazine, propyzamide, and diflufenican herbicides after repeated applications in fruit tree orchards.

机译:在果树园中多次施用后,敌草隆,氯甲苯隆,西马津,丙酰胺和双氟苯胺除草剂在土壤中的耗散。

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摘要

In a pear tree orchard planted on loam soil, each plot was treated in April 1998 with either one of the ureas diuron or chlorotoluron, or triazine simazine herbicides applied at 3, 4, and 2 kg AI ha(-1), respectively. Some plots had not been previously treated with one of these herbicides. Other plots had been treated annually during the past 12 years with the same herbicide. One herbicide, and always the same, was thus applied to each plot. In the plots treated for the first time with either diuron, chlorotoluron, or simazine, the soil half-lives of these herbicides in the 0-10 cm surface soil layer were 81, 64, and 59 days, respectively. In the plots treated with the same herbicide for 12 years, the corresponding soil half-lives were 37, 11, and 46 days. Diuron thus produced a moderately enhanced biodegradation, chlorotoluron a high one, and simazine a low but significant one. In another pear tree orchard planted on sandy loam soil, each plot was treated in April 1998 with one of the amide propyzamide (1.25 or 1.0 AI kg ha(-1)) or diflufenican (250 g AI ha(-1)) herbicides. In the plots not previously treated with propyzamide, the propyzamide soil half-life was the same for both doses, i.e., about 30 days. In the plots treated annually for 3 or 14 years with propyzamide, the soil half-life was 12 and 10 days, respectively. In the plots treated for the first time with diflufenican and in those treated annually with diflufenican for 3 years, the diflufenican soil half-life was the same, i.e., 65 days. Propyzamide thus already showed a highly accelerated biodegradation after 3 years of repeated annual applications. Diflufenican, however, did not show enhanced biodegradation after 3 years of repeated annual applications.
机译:在种植于壤土上的梨树果园中,每个地块均于1998年4月分别以3、4和2 kg AI ha(-1)施用脲二氮杂或氯甲苯隆或三嗪辛嗪除草剂中的一种。某些地块以前未使用其中一种除草剂处理过。在过去的12年中,其他地块每年都使用相同的除草剂进行处理。因此,将一种除草剂(并且始终相同)应用于每个地块。在首次用敌草隆,氯甲苯隆或西咪嗪处理的地块中,这些除草剂在0-10厘米表层土壤中的土壤半衰期分别为81天,64天和59天。在使用相同除草剂处理12年的地块中,相应的土壤半衰期分别为37天,11天和46天。因此,敌草隆产生了中等程度的增强的生物降解作用,氯甲苯隆产生了较高的降解速度,而辛嗪则产生了较低但显着的降解速度。在另一个种植在沙壤土上的梨树果园中,每个地块在1998年4月用酰胺基丙酰胺(1.25或1.0 AI kg ha(-1))或双氟替尼(250 g AI ha(-1))除草剂中的一种进行处理。在先前未用丙酰胺处理的地块中,两种剂量的丙酰胺土壤半衰期相同,即约30天。在每年用丙酰胺处理3或14年的地块中,土壤半衰期分别为12天和10天。在首次用双氟虫草处理的地块和每年用双氟虫草处理的地块中,双氟虫草的土壤半衰期是相同的,即65天。因此,丙吡酰胺在每年重复使用3年后已经显示出高度加速的生物降解作用。然而,在连续重复每年施用3年后,双氟芬尼没有表现出增强的生物降解作用。

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