Department of Plants, Soils, and Climate, Utah State University, Logan, Utah, USA.
Environ Toxicol Chem. 2013 Dec;32(12):2663-71. doi: 10.1002/etc.2344. Epub 2013 Oct 10.
Technical toxaphene, a broad-spectrum pesticide mixture, degrades in the environment, resulting in potential changes in toxicity. The present study uses a multimedia model that the authors developed to estimate toxaphene degradation in the atmosphere over North America. The predicted degradation has strong spatial and temporal variability determined by processes such as emission and transport of technical toxaphene, as well as the complex interactions among many species (e.g., toxaphene, hydroxyl [OH] radicals, and ozone). More toxaphene is degraded in warmer months due to higher concentrations of technical toxaphene (primarily due to higher technical toxaphene emissions in the southeastern United States and transport to other regions) and OH radicals. In the model, OH radicals are created primarily through the reactions of water vapor with the excited oxygen atom, O(¹D), generated by the photolysis of ozone, which is produced primarily by reactions of volatile organic compounds and nitrogen oxides (NOx) in the presence of sunlight. The higher OH concentrations in warmer months are primarily the result of higher solar radiation and ozone concentrations. The spatial distribution of degradation depends on the distribution of technical toxaphene soil residues as well as atmospheric transport and chemistry; significant chemical degradation occurs in the southeastern United States where soils are most heavily contaminated by past applications of toxaphene.
技术型硫丹是一种广谱杀虫剂混合物,会在环境中降解,从而导致其毒性可能发生变化。本研究使用了作者开发的多介质模型来估算北美地区大气中硫丹的降解情况。预测的降解具有很强的时空变异性,这是由技术型硫丹的排放和传输等过程以及许多物种(如硫丹、羟基[OH]自由基和臭氧)之间的复杂相互作用决定的。由于技术型硫丹浓度较高(主要是由于美国东南部技术型硫丹排放量较高,并输送到其他地区)和 OH 自由基较多,温暖月份的硫丹降解量更大。在模型中,OH 自由基主要通过水蒸气与由臭氧光解产生的激发态氧原子 O(¹D)之间的反应产生,臭氧主要由挥发性有机化合物和氮氧化物(NOx)在阳光存在下的反应产生。温暖月份较高的 OH 浓度主要是由于太阳辐射和臭氧浓度较高所致。降解的空间分布取决于技术型硫丹土壤残留物的分布以及大气传输和化学过程;在美国东南部,由于过去大量使用硫丹,土壤受到了最严重的污染,因此发生了大量的化学降解。