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土壤中农药降解简化假设的评估

Evaluation of simplifying assumptions on pesticide degradation in soil.

作者信息

Beulke Sabine, van Beinum Wendy, Brown Colin D, Mitchell Matthew, Walker Allan

机构信息

Cranfield Centre for EcoChemistry, Cranfield University, Silsoe, Bedford, UK.

出版信息

J Environ Qual. 2005 Oct 12;34(6):1933-43. doi: 10.2134/jeq2004.0460. Print 2005 Nov-Dec.

Abstract

There is evidence that degradation of pesticides in simple laboratory systems may differ from that in the field, but it is not clear which of the simplifications inherent in laboratory studies present serious shortcomings. Laboratory experiments evaluated several simplifying assumptions for a clay loam soil and contrasting pesticides. Degradation of cyanazine [2-(4-chloro-6-ethylamino-1,3,5-triazin-2-ylamino)-2-methylpropiononitrile] and bentazone [3-isopropyl-1H-2,1,3-benzothiadiazin-4(3H)-one 2,2-dioxide] at fluctuating temperature and moisture was predicted reasonably well based on parameters derived from degradation under constant conditions. There was a tendency for slower degradation of cyanazine and bentazone in soil aggregates of 3 to 5 mm in diameter (DT50 at 15 degrees C and 40% maximum water holding capacity of 25.1 and 58.2 d, where DT50 is the time for 50% decline of the initial pesticide concentration) than in soil sieved to <3 mm (DT50 of 19.1 and 37.6 d), but the differences were not significant for most datasets. Degradation of cyanazine, isoproturon [3-(4-isopropylphenyl)-1,1-dimethylurea], and chlorotoluron [3-(3-chloro-p-tolyl)-1,1-dimethylurea] was measured in soil amended with different amounts of lignin. The effect of lignin on degradation was small despite considerable differences in sorption. The DT50 values of cyanazine, isoproturon, and chlorotoluron were 16.2, 18.6, and 33.0 d, respectively, in soil without lignin and 19.0, 23.4, and 34.6 d, respectively, in soil amended with 2% lignin. Degradation of bentazone and cyanazine in repacked soil columns was similar under static and flow conditions with 50.1 and 47.2% of applied bentazone and 74.7 and 73.6% of applied cyanazine, respectively, degraded within 20 d of application. Thus, the assumptions underpinning laboratory to field extrapolation tested here were considered to hold for our experimental system. Additional work is required before general conclusions can be drawn.

摘要

有证据表明,农药在简单实验室系统中的降解情况可能与在田间不同,但尚不清楚实验室研究中固有的哪些简化方法存在严重缺陷。实验室实验评估了针对一种粘壤土和不同农药的几种简化假设。基于在恒定条件下得出的参数,对温度和湿度波动时嗪草酮[2-(4-氯-6-乙基氨基-1,3,5-三嗪-2-基氨基)-2-甲基丙腈]和苯达松[3-异丙基-1H-2,1,3-苯并噻二嗪-4(3H)-酮2,2-二氧化物]的降解进行了较为合理的预测。在直径为3至5毫米的土壤团聚体中,嗪草酮和苯达松的降解有变慢的趋势(在15摄氏度和最大持水量40%时,DT50分别为25.1天和58.2天,其中DT50是初始农药浓度下降50%的时间),相比之下,过筛至<3毫米的土壤中DT50分别为19.1天和37.6天,但对于大多数数据集而言,差异并不显著。在添加了不同量木质素的土壤中测量了嗪草酮、异丙隆[3-(4-异丙苯基)-1,1-二甲基脲]和绿麦隆[3-(3-氯对甲苯基)-1,1-二甲基脲]的降解情况。尽管吸附存在显著差异,但木质素对降解的影响较小。在未添加木质素的土壤中,嗪草酮、异丙隆和绿麦隆的DT50值分别为16.2天、18.6天和33.0天,在添加2%木质素的土壤中分别为19.0天、23.4天和34.6天。在重新装填的土柱中,苯达松和嗪草酮在静态和流动条件下的降解情况相似,施药后20天内,分别有50.1%和47.2%的施入苯达松以及74.7%和73.6%的施入嗪草酮发生降解。因此,这里测试的从实验室推断到田间的假设被认为适用于我们的实验系统。在得出一般性结论之前,还需要开展更多工作。

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