Pesticide Residue Laboratory, ICAR-Indian Institute of Horticultural Research, Hesaraghatta Lake P.O., Bangalore, Karnataka, 560089, India.
Center for Postgraduate Studies (Jain University), 18/3, 9th Main, 3rd Block, Jayanagar, Bangalore, 560011, India.
Environ Sci Pollut Res Int. 2017 Oct;24(30):23559-23570. doi: 10.1007/s11356-017-9954-9. Epub 2017 Aug 29.
Dissipation of spiromesifen and its metabolite, spiromesifen-enol, on tomato fruit, tomato leaf, and soil was studied in the open field and controlled environmental conditions. Sample preparation was carried out by QuEChERS method and analysis using LC-MS/MS. Method validation for analysis of the compounds was carried out as per "single laboratory method validation guidelines." Method validation studies gave satisfactory recoveries for spiromesifen and spiromesifen-enol (71.59-105.3%) with relative standard deviation (RSD) < 20%. LOD and LOQ of the method were 0.0015 μg mL and 0.005 mg kg, respectively. Spiromesifen residues on tomato fruits were 0.855 and 1.545 mg kg in open field and 0.976 and 1.670 mg kg under polyhouse condition, from treatments at the standard and double doses of 125 and 250 g a.i. ha, respectively. On tomato leaves, the residues were 5.64 and 8.226 mg kg in open field and 6.874 and 10.187 mg kg in the polyhouse. In soil, the residues were 0.532 and 1.032 mg kg and 0.486 and 0.925 mg kg under open field and polyhouse conditions, respectively. The half-life of degradation of spiromesifen on tomato fruit was 6-6.5 days in the open field and 8.1-9.3 days in the polyhouse. On tomato leaves, it was 7-7.6 and 17.6-18.4 days and in soil 5.6-7.4 and 8.4-9.5 days, respectively. Metabolite, spiromesifen-enol, was not detected in any of the sample throughout the study period. Photodegradation could be the major route for dissipation of spiromesifen in the tomato leaves, whereas in the fruits, it may be the combination of photodegradation and dilution due to fruit growth. The results of the study can be utilized for application of spiromesifen in plant protection of tomato crop under protected environmental conditions.
在田间和控制环境条件下,研究了螺虫乙酯及其代谢物螺虫乙酯-烯醇在番茄果实、番茄叶片和土壤中的消解情况。样品制备采用 QuEChERS 法,使用 LC-MS/MS 进行分析。化合物分析的方法验证按照“单实验室方法验证指南”进行。方法验证研究表明,螺虫乙酯和螺虫乙酯-烯醇的回收率令人满意(71.59-105.3%),相对标准偏差(RSD)<20%。方法的检出限和定量限分别为 0.0015μg mL 和 0.005mg kg。在田间条件下,标准剂量和双倍剂量(125 和 250g a.i. ha)处理后,番茄果实上的螺虫乙酯残留量分别为 0.855 和 1.545mg kg,聚温室条件下分别为 0.976 和 1.670mg kg。在番茄叶片上,田间和聚温室条件下的残留量分别为 5.64 和 8.226mg kg,6.874 和 10.187mg kg。在土壤中,田间和聚温室条件下的残留量分别为 0.532 和 1.032mg kg,0.486 和 0.925mg kg。螺虫乙酯在番茄果实上的半衰期在田间为 6-6.5 天,在聚温室中为 8.1-9.3 天。在番茄叶片上,半衰期分别为 7-7.6 天和 17.6-18.4 天,在土壤中分别为 5.6-7.4 天和 8.4-9.5 天。在整个研究期间,都未在任何样品中检测到代谢物螺虫乙酯-烯醇。光降解可能是螺虫乙酯在番茄叶片中消解的主要途径,而在果实中,可能是光降解和果实生长导致的稀释共同作用的结果。研究结果可用于指导在保护地环境条件下使用螺虫乙酯对番茄作物进行病虫害防治。