Division of Agricultural Chemicals, Indian Agricultural Research Institute, New Delhi, India.
Bull Environ Contam Toxicol. 2011 Sep;87(3):292-6. doi: 10.1007/s00128-011-0333-9. Epub 2011 Jun 17.
Persistence of flubendiamide in soil as affected by UV and sunlight exposure and in water as affected by pH was studied. At field capacity moisture regime, soil was treated with flubendiamide and exposed to UV and sunlight. Dissipation for the pesticide followed mono-phasic first order kinetics. Residues of flubendiamide, as thin film on petri-plates and soil thin film, dissipated with half-lives of 7.0 and 9.1 days under UV light and 12.0 and 19.1 days under sunlight, respectively. Residues of flubendiamide dissipated faster under UV light as compared to sunlight. Persistence study in aqueous medium under different pH condition indicated that flubendiamide residues persisted in water beyond 250 days with half-lives ranging from 250.8 to 301.0 days. Dissipation in water was faster at pH 4.0 (T(1/2) 250.8 days), followed by pH 9.2 (T(1/2) 273.6 days) and 7.0 (T(1/2) 301.0 days).
本研究考察了紫外线和阳光照射对土壤中氟苯虫酰胺持久性的影响,以及 pH 值对水中氟苯虫酰胺持久性的影响。在田间持水量的水分条件下,用氟苯虫酰胺处理土壤并暴露于紫外线和阳光之下。农药的消解遵循单相位一级动力学。在紫外线照射下,氟苯虫酰胺在培养皿薄膜和土壤薄膜上的残留分别以 7.0 和 9.1 天的半衰期消散;在阳光照射下,残留分别以 12.0 和 19.1 天的半衰期消散。与阳光相比,紫外线照射下氟苯虫酰胺的残留消解更快。在不同 pH 值条件下的水相持久性研究表明,氟苯虫酰胺在水中的残留超过 250 天,半衰期范围为 250.8 至 301.0 天。在 pH 值为 4.0(T(1/2) 250.8 天)时,水中的消解速度最快,其次是 pH 值为 9.2(T(1/2) 273.6 天)和 7.0(T(1/2) 301.0 天)。