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螺虫乙酯及其代谢产物在猕猴桃中的残留消解动态
引用本文:黄玉南,乔成奎,庞涛,罗静,庞荣丽,郭琳琳,李君,王瑞萍,谢汉忠.螺虫乙酯及其代谢产物在猕猴桃中的残留消解动态[J].现代食品科技,2018,34(12):221-227.
作者姓名:黄玉南  乔成奎  庞涛  罗静  庞荣丽  郭琳琳  李君  王瑞萍  谢汉忠
作者单位:(1.中国农业科学院郑州果树研究所,农业部果品质量安全风险评估实验室(郑州),河南郑州 450009) (2.中检溯源江苏技术服务有限公司,江苏南京 211215),(1.中国农业科学院郑州果树研究所,农业部果品质量安全风险评估实验室(郑州),河南郑州 450009),(1.中国农业科学院郑州果树研究所,农业部果品质量安全风险评估实验室(郑州),河南郑州 450009),(1.中国农业科学院郑州果树研究所,农业部果品质量安全风险评估实验室(郑州),河南郑州 450009),(1.中国农业科学院郑州果树研究所,农业部果品质量安全风险评估实验室(郑州),河南郑州 450009),(1.中国农业科学院郑州果树研究所,农业部果品质量安全风险评估实验室(郑州),河南郑州 450009),(1.中国农业科学院郑州果树研究所,农业部果品质量安全风险评估实验室(郑州),河南郑州 450009),(1.中国农业科学院郑州果树研究所,农业部果品质量安全风险评估实验室(郑州),河南郑州 450009),(1.中国农业科学院郑州果树研究所,农业部果品质量安全风险评估实验室(郑州),河南郑州 450009)
基金项目:中国农业科学院创新工程科技经费项目资助(CAAS-ASTIP-2018- ZFRI);国家农产品质量安全风险评估专项(GJFP2018003)
摘    要:研究建立了螺虫乙酯及其4种主要代谢物在猕猴桃及土壤中的残留分析方法。样品用乙腈提取后,经PSA净化,高效液相色谱质谱联用仪检测,外标法定量。结果表明:在0.01~2.00mg/kg的添加水平下,螺虫乙酯及代谢产物在猕猴桃和土壤中的回收率为73.97%~110.52%,相对标准偏差分别为1.96%~7.91%。采用所建方法,测定螺虫乙酯及代谢产物在猕猴桃和土壤中的残留及消解动态。螺虫乙酯被施用到猕猴桃和土壤中后均迅速降解为B-enol、B-keto。在猕猴桃中螺虫乙酯、B-enol呈逐渐降低的趋势,而B-keto和B-mono呈逐渐升高的趋势;在土壤中螺虫乙酯、B-enol、B-keto均呈逐渐降低趋势,B-mono和B-glu在样品中均没有检出。螺虫乙酯和B-enol在土壤中的降解速度(1.42 d、1.99 d)快于在猕猴桃上的降解速度(4.08 d和6.39 d)。以3000倍液稀释液喷施2次,28 d后,猕猴桃中螺虫乙酯母体的残留量为0.06 mg/kg,高于我国制定的0.02 mg/kg的最大残留限量值,在猕猴桃上的安全使用剂量还需要进一步研究。

关 键 词:螺虫乙酯  猕猴桃  土壤  残留  消解动态
收稿时间:2018/8/13 0:00:00

Residue and Dissipation of Spirotetramat and Its Metabolites in Kiwifruits and Soil
HUANG Yu-nan,QIAO Cheng-kui,PANG Tao,LUO Jing,PANG Rong-li,GUO Lin-lin,LI Jun,WANG Rui-ping and XIE Han-zhong.Residue and Dissipation of Spirotetramat and Its Metabolites in Kiwifruits and Soil[J].Modern Food Science & Technology,2018,34(12):221-227.
Authors:HUANG Yu-nan  QIAO Cheng-kui  PANG Tao  LUO Jing  PANG Rong-li  GUO Lin-lin  LI Jun  WANG Rui-ping and XIE Han-zhong
Affiliation:(1.Institute of Zhengzhou Pomology, CAAS/ Laboratory of Quality & Safety Risk Assessment for Fruit (Zhengzhou), Ministry of Agriculture, Zhengzhou 450009, China) (2.CCIC Traceability Jiangsu Technology Service Co., Ltd, Nanjing 211215, China),(1.Institute of Zhengzhou Pomology, CAAS/ Laboratory of Quality & Safety Risk Assessment for Fruit (Zhengzhou), Ministry of Agriculture, Zhengzhou 450009, China),(1.Institute of Zhengzhou Pomology, CAAS/ Laboratory of Quality & Safety Risk Assessment for Fruit (Zhengzhou), Ministry of Agriculture, Zhengzhou 450009, China),(1.Institute of Zhengzhou Pomology, CAAS/ Laboratory of Quality & Safety Risk Assessment for Fruit (Zhengzhou), Ministry of Agriculture, Zhengzhou 450009, China),(1.Institute of Zhengzhou Pomology, CAAS/ Laboratory of Quality & Safety Risk Assessment for Fruit (Zhengzhou), Ministry of Agriculture, Zhengzhou 450009, China),(1.Institute of Zhengzhou Pomology, CAAS/ Laboratory of Quality & Safety Risk Assessment for Fruit (Zhengzhou), Ministry of Agriculture, Zhengzhou 450009, China),(1.Institute of Zhengzhou Pomology, CAAS/ Laboratory of Quality & Safety Risk Assessment for Fruit (Zhengzhou), Ministry of Agriculture, Zhengzhou 450009, China),(1.Institute of Zhengzhou Pomology, CAAS/ Laboratory of Quality & Safety Risk Assessment for Fruit (Zhengzhou), Ministry of Agriculture, Zhengzhou 450009, China) and (1.Institute of Zhengzhou Pomology, CAAS/ Laboratory of Quality & Safety Risk Assessment for Fruit (Zhengzhou), Ministry of Agriculture, Zhengzhou 450009, China)
Abstract:This paper developed a rapid method for analyzing the spirotetramat and its four major metabolites residues in kiwifruits and soil. Samples were extracted with acetonitrile, cleaned up by Solid Phase Extraction PSA and detected by using high performance liquid chromatography-tandem mass spectrometry. Average recoveries of spirotetramat and its four major metabolites fortified at 0.01~2.00 mg/kg in kiwifruits and soil ranged from 73.97%~110.52% with the relative standard deviations (RSD) of 1.96%~7.91%, respectively. Using the above method, residue dissipation of spirotetramat and its metabolites in kiwifruits and soil were detected. After spirotetramat is applied to the soil and kiwi, it was rapidly degraded as B-enol, B-keto. In the kiwifruit, the spirotetramat and B-enol gradually decreased, while the B-keto and B-mono showed a gradual increase. In the soil, spirotetramat, B-enol and B-keto showed a decreasing trend, and B-mono and B-glu were not detected in the samples. The degradation rates of spirotetramat and B-enol in soil (1.42 d and 1.99 d, respectively) were faster than those on kiwifruit (4.08 d and 6.39 d, respectively). Sprayed twice with 3000 times liquid dilution, after 28 days, the residual amount of spirotetramat in kiwifruit was 0.06 mg/kg, which was higher than the maximum residue limit of 0.02 mg/kg formulated in China, the safe use of kiwifruit requires further study.
Keywords:spirotetramat  kiwifruit  soil  residue  dissipation
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