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田间条件下精喹禾灵除草剂在向日葵种植中的消散与迁移

Dissipation and transport of quizalofop-p-ethyl herbicide in sunflower cultivation under field conditions.

作者信息

Mantzos Nikolaos, Karakitsou Anastasia, Nikolaki Sofia, Leneti Eleni, Konstantinou Ioannis

机构信息

Department of Environmental and Natural Resources Management, University of Patras, Agrinio, Greece.

Faculty of Agricultural Technology, T.E.I. of Epirus, Arta, Greece.

出版信息

Environ Sci Pollut Res Int. 2016 Feb;23(4):3481-90. doi: 10.1007/s11356-015-5572-6. Epub 2015 Oct 21.

Abstract

In the present study, the field dissipation and transport of quizalofop-p-ethyl by water and sediment runoff were investigated in sunflower experimental cultivation under Mediterranean conditions. The cultivation was carried out in silty clay soil plots with two different slopes of 1 and 5%. The soil dissipation rate of quizalofop-p-ethyl was fast and can be described by both single first-order (SFO) and Gustafson and Holden (first-order multi compartment (FOMC)) kinetics. The half-life of quizalofop-p-ethyl ranged from 0.55 to 0.68 days and from 0.45 to 0.71 days when SFO and FOMC kinetics were applied, respectively. No herbicide residues were detected below the 10-cm soil layer. A single detection of quizalofop-p-ethyl was observed in runoff water (3 days after application (DAA)) at relatively low concentrations (from 1.70 to 2.04 μg L(-1)). In sediment, it was detected in the samplings of 3 and 25 DAA at concentrations that never exceeded 0.126 μg g(-1). The estimated total losses of quizalofop-p-ethyl as percentage of the initial applied active ingredient were low both in water and sediment (less than of 0.021 and 0.005%, respectively). Quizalofop-p-ethyl residues were detectable for 18 DAA in the stems and leaves of the plants and 6 DAA in the root system. No herbicide residues were detected in inflorescences and seeds of sunflower plants. Experimental data showed minimal risk for the contamination of soil and adjacent water bodies.

摘要

在本研究中,在地中海条件下的向日葵试验种植中,研究了精喹禾灵 - p - 乙基通过水和泥沙径流的田间消散与迁移情况。种植在粉质粘土壤地块中进行,坡度分别为1%和5%。精喹禾灵 - p - 乙基在土壤中的消散速率很快,可用单一级动力学(SFO)以及古斯塔夫森和霍尔登的一级多室动力学(FOMC)来描述。当应用SFO和FOMC动力学时,精喹禾灵 - p - 乙基的半衰期分别为0.55至0.68天和0.45至0.71天。在10厘米以下的土壤层未检测到除草剂残留。在径流水中(施药后3天(DAA))检测到一次精喹禾灵 - p - 乙基,浓度相对较低(1.70至2.04微克/升)。在沉积物中,在施药后3天和25天的采样中检测到该物质,浓度从未超过0.126微克/克。精喹禾灵 - p - 乙基作为初始施用活性成分的百分比计算得出的总损失在水和沉积物中都很低(分别小于0.021%和0.005%)。精喹禾灵 - p - 乙基残留在植物的茎和叶中可检测18天,在根系中可检测6天。在向日葵植株的花序和种子中未检测到除草剂残留。实验数据表明土壤和相邻水体受污染的风险极小。

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