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Previous degradation study of two herbicides to simulate their fate in a sandy loam soil: Effect of the temperature and the organic amendments

机译:先前在沙质壤土中模拟两种除草剂的降解研究:温度和有机改性剂的影响

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A laboratory study was designed to assess the following: i) the degradation kinetics of chlorotoluron and flufenacet at two different temperatures, 6 degrees C and 16 degrees C, in an unamended agricultural soil and one amended with spent mushroom substrate (SMS) and green compost (GC), and ii) the formation of the main metabolites of both herbicides with potential risk for water pollution over degradation time. The aim was to determine the dependence of these herbicide degradations on temperature (Q(10) factor) using kinetic parameters, which is essential information for the later simulation of herbicide environmental fate with FOCUS models. SMS and GC were applied in situ to the natural soil as organic amendments at rates of 140 or 85 t residue ha(-1), respectively. Unamended and amended soils were taken from the 0-10 cm topsoil of experimental plots (three replicates/treatment) located on an agricultural farm. Samples of soil + herbicides were incubated at 6 degrees C or 16 degrees C under laboratory conditions. The degradation curves of chlorotoluron and flufenacet were fitted to single first-order and first-order multicompartment kinetic models, respectively. The flufenacet degradation, the more hydrophobic herbicide, was slower than that of chlorotoluron in all the treatments. The application of the organic amendments to soil increased the half-lives (DT50) for both herbicides incubated at 6 degrees C (1.3-1.9 times) and 16 degrees C (1.4-1.9 times) due to their higher sorption and lower bioavailability for degradation in amended soils. The herbicides recorded a faster degradation at 16 degrees C than at 6 degrees C (Q(10)=1.9-2.8) due to the increased microbial biomass and/or activity with temperature. The metabolites desmethyl chlorotoluron, flufenacet ESA and flufenacet OA were detected in all the soil treatments at both incubation temperatures. The determination of Q(10) factors in amended soils is very valuable for generating accurate input data for pesticide fate models such as FOCUS in order to improve the evaluation of the leaching of herbicides and their transformation products, which is a relevant goal to maintain the sustainability of agricultural systems. (c) 2018 Elsevier B.V. All rights reserved.
机译:设计了一项实验室研究来评估以下各项:i)在未经修正的农业土壤中,在6摄氏度和16摄氏度的两种不同温度下,氯代甲苯隆和氟苯乙酰胺的降解动力学,以及用废蘑菇基质(SMS)和绿色堆肥进行修正的降解动力学(GC),以及ii)两种除草剂的主要代谢物的形成,它们在降解时间内可能会污染水。目的是使用动力学参数确定这些除草剂降解对温度(Q(10)因子)的依赖性,这对于以后使用FOCUS模型模拟除草剂的环境命运是必不可少的信息。 SMS和GC分别以140或85 t残留ha(-1)的比例原位施用于天然土壤作为有机改良剂。未经修改和修改过的土壤取自位于农业农场的实验区(10个重复/处理)的0-10厘米表土。在实验室条件下,将土壤+除草剂样品在6摄氏度或16摄氏度下孵育。氯甲苯和氟苯乙酰胺的降解曲线分别拟合到单个一阶和一阶多室动力学模型。在所有处理中,氟草酸降解物(疏水性更强的除草剂)均比氯甲苯隆的降解速度慢。有机改性剂在土壤上的应用增加了两种除草剂在6摄氏度(1.3-1.9倍)和16摄氏度(1.4-1.9倍)下孵育的半衰期(DT50),这是因为它们具有较高的吸附能力和较低的降解生物利用度在改良土壤中。由于微生物生物量和/或活性随温度升高,除草剂在16摄氏度下的降解速度比6摄氏度下更快(Q(10)= 1.9-2.8)。在两个培养温度下,在所有土壤处理中均检测到了代谢物脱甲基氯甲苯隆,氟苯乙酰胺ESA和氟苯乙胺OA。确定改良土壤中的Q(10)因子对于为农药命运模型(如FOCUS)生成准确的输入数据,以改善对除草剂及其转化产物的浸出的评估,是非常有价值的,这是维持农药的相关目标。农业系统的可持续性。 (c)2018 Elsevier B.V.保留所有权利。

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