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杀菌剂戊唑醇的光转化及其在阳光照表面淡水中的预测归宿。

Phototransformation of the fungicide tebuconazole, and its predicted fate in sunlit surface freshwaters.

机构信息

Dipartimento di Chimica, Università degli Studi di Torino, Via Pietro Giuria 5, 10125, Torino, Italy.

Dipartimento di Chimica, Università degli Studi di Torino, Via Pietro Giuria 5, 10125, Torino, Italy.

出版信息

Chemosphere. 2022 Sep;303(Pt 2):134895. doi: 10.1016/j.chemosphere.2022.134895. Epub 2022 May 11.

Abstract

The fungicide tebuconazole (TBCZ) is expected to undergo negligible direct photolysis in surface freshwaters, but it can be degraded by indirect photochemistry. TBCZ mainly reacts with hydroxyl radicals and, to a lesser extent, with the triplet states of chromophoric dissolved organic matter (CDOM*). Indirect photochemistry is strongly affected by environmental conditions, and TBCZ lifetimes of about one week are expected in sunlit surface waters under favourable circumstances (shallow waters with low concentrations of dissolved organic carbon, DOC, during summer). In these cases, the time trend would follow pseudo-first order kinetics (mono-exponential decay). Under less favourable conditions, photoinduced degradation would span over a few or several months, and TBCZ phototransformation would depart from an exponential trend because of seasonally changing sunlight irradiance. The TBCZ phototransformation products should be less toxic than their parent compound,thus photodegradation has potential to decrease the environmental impact of TBCZ. Hydroxylation is a major TBCZ transformation route, due to either OH attack, or one-electron oxidation sensitised by CDOM*, followed by reaction of the oxidised transient with oxygen and water.

摘要

杀菌剂戊唑醇(TBCZ)预计在地表淡水中不会发生显著的直接光解,但可通过间接光化学降解。TBCZ 主要与羟基自由基反应,在较小程度上与发色溶解有机物(CDOM*)的三重态反应。间接光化学受环境条件强烈影响,在有利条件下(夏季浅水、低浓度溶解有机碳(DOC)),TBCZ 在阳光照射的地表水中的半衰期约为一周。在这些情况下,时间趋势将遵循准一级动力学(单指数衰减)。在条件较差的情况下,光诱导降解将持续数天或数月,由于季节性变化的阳光辐照度,TBCZ 的光转化将偏离指数趋势。TBCZ 的光转化产物的毒性应低于其母体化合物,因此光降解有可能降低 TBCZ 的环境影响。由于 CDOM* 的 OH 攻击或单电子氧化敏化,导致羟基化是 TBCZ 的主要转化途径,然后氧化瞬态与氧气和水反应。

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