Syngenta, Jealott's Hill International Research Centre, Bracknell, Berkshire RG42 6EY, United Kingdom.
Environ Toxicol Chem. 2010 Dec;29(12):2702-12. doi: 10.1002/etc.337. Epub 2010 Oct 1.
Degradation of a new fungicide, isopyrazam, was slow in water-sediment systems maintained in the dark, with degradation half-life (DegT50) values in the total system (water column and sediment) of greater than one year, and only moderately fast in a photolysis study in buffered pure water (DegT50 > 60 d). This indicated that microbial degradation and direct photolysis are not significant loss mechanisms for this compound. Under more realistic conditions, a number of other processes of natural attenuation occur, such as metabolism by aquatic plants, microalgae, and periphyton and indirect photolysis. A photolysis study in sterile natural water, and water-sediment studies incorporating aquatic macrophytes and microalgae under fluorescent light, were therefore conducted to investigate the contribution of these processes to the fate of isopyrazam. Degradation rates were at least one order of magnitude faster in these higher-tier laboratory studies, indicating that all of these processes may have a role to play in complex natural ecosystems. The fate in an outdoor system, designed to mimic conditions in edge-of-field drainage ditches, also was investigated to provide an integrated picture of the contribution of all the different potential loss mechanisms to the overall fate of isopyrazam. The total system DegT50 in the study was similar to that observed in the higher-tier laboratory studies. Furthermore, the pattern of degradation formation allowed for the contribution of the different degradation processes at work in the microcosm study to be contextualized. The implementation of this tiered approach to investigating the aquatic fate of crop protection products provides a comprehensive explanation of the behavior of isopyrazam and clearly demonstrates that it will not persist in the aquatic environment under natural conditions.
在黑暗中维持的水-沉积物系统中,新型杀菌剂异恶唑草酮的降解速度缓慢,总系统(水柱和沉积物)中的降解半衰期(DegT50)值大于一年,而在缓冲纯水中的光解研究中则降解速度适中较快(DegT50>60d)。这表明微生物降解和直接光解不是该化合物的主要损失机制。在更现实的条件下,还会发生许多其他自然衰减过程,例如水生植物、微藻和周丛生物的代谢以及间接光解。因此,进行了无菌天然水的光解研究以及包含水生大型植物和微藻的水-沉积物研究,以荧光灯为光源,以研究这些过程对异恶唑草酮命运的贡献。在这些更高层次的实验室研究中,降解速率至少快了一个数量级,这表明所有这些过程都可能在复杂的自然生态系统中发挥作用。还研究了在户外系统中的命运,该系统旨在模拟田间边缘排水渠的条件,以提供所有不同潜在损失机制对异恶唑草酮总体命运的贡献的综合情况。研究中的总系统 DegT50 与在更高层次的实验室研究中观察到的相似。此外,降解产物的形成模式允许将微宇宙研究中起作用的不同降解过程的贡献置于上下文中。采用这种分层方法来研究作物保护产品在水中的命运,可以全面解释异恶唑草酮的行为,并清楚地表明,在自然条件下,它不会在水生环境中持久存在。