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二嗪磷挥发的日变化:土壤湿度的影响。

Diurnal variation of diazinon volatilization: soil moisture effects.

机构信息

Land, Air and Water Resources, University of California, One Shield Avenue, Davis, California 95616, United States.

出版信息

Environ Sci Technol. 2011 Mar 15;45(6):2144-9. doi: 10.1021/es102921r. Epub 2011 Feb 14.

Abstract

Diurnal variations in diazinon volatilization were monitored in three field experiments conducted with differing soil moisture contents. The highest flux rates in all experiments were recorded just after diazinon application, but the magnitudes of those initial rates differed according to the soil moisture content, with wetter soil producing a higher rate: 5.6 × 10(-4) μg cm(-2) min(-1) for initial soil moisture above field capacity, 8.3 × 10(-5) μg cm(-2) min(-1) for initial soil moisture at field capacity, and 2.5 × 10(-5) μg cm(-2) min(-1) for initially very dry soil. Volatilization decreased during the first day in the two experiments with initially wet soils but remained relatively constant in the experiment with initially dry soil. The volatilization rate during the first night for the wettest soil remained about an order-of-magnitude higher than that observed for driest soil. When the surface dried in the experiment conducted at the intermediate water content, the volatilization rate and temporal pattern transitioned and became similar to that observed for the initially dry soil. Around noon of the second day, a daily maximum value was observed in the volatilization rate for wet soil, whereas a minimum value was observed for the dry soil, resulting in an order-of magnitude difference. This study demonstrates the importance of soil moisture on emissions of pesticides to the atmosphere.

摘要

本研究在三个田间试验中监测了二嗪磷挥发的日变化,这些试验的土壤湿度条件不同。在所有试验中,施药后立即记录到的通量速率最高,但初始速率的大小因土壤湿度而异,较湿的土壤产生更高的速率:初始土壤含水量高于田间持水量时为 5.6×10(-4)μg cm(-2) min(-1),初始土壤含水量为田间持水量时为 8.3×10(-5)μg cm(-2) min(-1),初始非常干燥的土壤时为 2.5×10(-5)μg cm(-2) min(-1)。在最初较湿的两个试验中,施药后第一天挥发量减少,但在最初较干燥的试验中挥发量相对稳定。最湿土壤的第一个夜晚的挥发速率仍然比最干燥土壤观察到的速率高约一个数量级。当中间水分含量试验中的表面变干时,挥发速率和时间模式发生转变,变得与最初干燥土壤的情况相似。第二天中午左右,湿土的挥发速率出现日最大值,而干土的挥发速率出现最小值,两者相差一个数量级。这项研究表明了土壤湿度对农药向大气排放的重要性。

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