CERNAS, Department of Basic Sciences, ESAC, Bencanta, 3040-316 Coimbra, Portugal.
Chemosphere. 2013 May;91(7):993-1001. doi: 10.1016/j.chemosphere.2013.01.092. Epub 2013 Mar 7.
In this study, the relevance of photodegradation processes on the persistence of the fungicide thiram in waters was investigated. The photodegradation of thiram in Milli-Q water and in aqueous solutions of humic and fulvic acids, as well as the photodegradation in spiked river water were studied. Both pure thiram and one of its commercial formulations were used to prepare the solutions which were irradiated in a solar light simulator. In general, thiram photodegradation follows pseudo-first order kinetics. The half-life time of thiram 2mgL(-1) in Milli-Q water was 28min. However, the degradation rate of thiram was significantly increased (p=0.02) by the inert components of the thiram commercial formulation as well as by commercial humic acids and by fulvic acids isolated from river water (p<0.004). Thus, the half-life time of thiram decreased to 24min in the presence of the inert formulation components, while, in the presence of both humic and fulvic acids (10mgL(-1)) it decreased to 22min. Furthermore, thiram photodegradation in natural river water showed that there is a significant enhancement of the degradation rate constant of thiram relatively to Milli-Q water, corresponding to a decrease of about 38% in its half-life time. This increase of the degradation rate in river water seems to be higher than that observed in the presence of FA, suggesting that beyond organic matter, other natural river components can increase the thiram photodegradation rate. These results allow us to conclude that photodegradation by solar radiation can be an important degradation pathway of thiram in natural waters. HPLC-MS/MS allowed to identify, for the first time, three products of the photodegradation of thiram in aqueous solution. Three compounds were identified and their structure was corroborated by the MS(n) spectra fragmentation profile. Pathways for the formation of the products from thiram photodegradation are proposed and discussed.
本研究调查了光降解过程对杀菌剂福美双在水中持久性的相关性。研究了福美双在 Milli-Q 水和腐殖酸及富里酸水溶液中的光降解,以及在加标河水的光降解。使用纯福美双和一种其商业制剂来制备溶液,并在太阳模拟器中进行辐照。一般来说,福美双光降解遵循假一级动力学。Milli-Q 水中 2mgL(-1)福美双的半衰期为 28min。然而,福美双商业制剂的惰性成分以及商业腐殖酸和从河水中分离出的富里酸显著增加了福美双的降解速率(p=0.02)。因此,在惰性制剂成分存在下,福美双的半衰期缩短至 24min,而在腐殖酸和富里酸(10mgL(-1))存在下,半衰期缩短至 22min。此外,天然河水中的福美双光降解表明,与 Milli-Q 水相比,福美双的降解速率常数有显著提高,相应地其半衰期缩短了约 38%。河水中降解速率的增加似乎高于在 FA 存在下观察到的增加,这表明除了有机物之外,其他天然河成分可以提高福美双的光降解速率。这些结果表明,太阳辐射的光降解可能是福美双在天然水中的重要降解途径。HPLC-MS/MS 首次在水溶液中鉴定出福美双光降解的三种产物。鉴定了三种化合物,并通过 MS(n)谱碎片特征证实了它们的结构。提出并讨论了产物形成的途径。