• Title/Summary/Keyword: dislodgeable residue

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Persistence and Dislodgeable Residues of Chlorpyrifos and Procymidone in Lettuce Leaves under Greenhouse Condition (상추의 생산단계별 Chlorpyrifos 및 Procymidone의 잔류허용기준 설정)

  • Kim, Young-Sook;Park, Ju-Hwang;Park, Jong-Woo;Lee, Young-Deuk;Lee, Kyu-Seung;Kim, Jang-Eok
    • Korean Journal of Environmental Agriculture
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    • v.21 no.2
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    • pp.149-155
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    • 2002
  • Two pesticides commonly used for lettuce cultivation including chlorpyrifos and procymidone were subjected to a field residue trial to ensure safety of terminal residues in the harvest. After pesticides were applied at standard and double rates in a foliar spray, leaf persistence of their residues was investigated far 10 days prior to harvest. Even though far exceeded the tolerances, initial leaf residues were rapidly dissipated with time and remained only 0.4$\sim$7.2% of the residues in the harvest. As well fitted by the first-order kinetics, biological half-lives of the pesticide residues in lettuce leaves ranged 1.2$\sim$2.6 days. Slow dissipation of the residues in the harvest was observed during storage at room temperature and 4$^{\circ}C$ for 7 days. Portions of dislodgeable residues which resided in detergent washings decreased as time elapsed. Patterns in dissipation and distribution of dislodgeable residues were not largely affected by the application rate of pesticides. It is concluded that timing of pesticide application, that is, pre-harvest interval would be the first factor to determine the terminal residue level in edible portions of lettuce.

Residues and Half-lives of Bitertanol and Tebuconazole in Greenhouse-Grown Peppers (시설재배 고추중 Bitertanol 및 Tebuconazole 잔류양상)

  • Seong, Ki-Yong;Jeong, Mong-Hee;Hur, Jang-Hyun;Kim, Jeong-Gyu;Lee, Kyu-Seung;Choi, Kyu-Il
    • Applied Biological Chemistry
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    • v.47 no.1
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    • pp.113-119
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    • 2004
  • Persistence of the triazole fungicides, bitertanol and tebucnazole was investigated after their application at recommended and double rate on greenhouse-grown peppers. The half-life of bitertanol and tebuconazole on peppers at recommended and double rate was $5.2{\sim}6.1$ and $4.6{\sim}5.2$ days, respectively. Half-lives of bitertanol and tebuconazole on pepper leaves $(16.8{\sim}22.5\;days)$ was longer than those in the peppers. Residual concentration of bitertanol and tebuconazole on pepper leaves 24 days after application were 10.1 and 17.5 mg/kg, respectively, and these levels were higher than MRL which had been established at 3.0 and 5.0 mg/kg in Korea. Pattern of dissipation was well fitted to the first-order kinetics. In household washing experiment with surfactant, dislodgeable portions on pepper leaves of bitertanol and tebuconazole were occupied 36% and 48% of the residues found 24 days after application.

Risk Assessment of Fipronil on Honeybee (Apis mellifera) (Fipronil의 꿀벌 (Apis mellifera)에 대한 위해성 평가)

  • Kim, Byung-Seok;Yang, Yu-Jung;Park, Yeon-Ki;Jeong, Mi-Hye;You, Are-Sun;Park, Kyung-Hun;Ahn, Young-Joon
    • The Korean Journal of Pesticide Science
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    • v.13 no.1
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    • pp.39-44
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    • 2009
  • This study was conducted to evaluate the actual risk of fipronil on worker honey bees (Apis mellifera L.) through acute contact toxicity test, acute oral toxicity test, toxicity of residues on foliage test, and small scale field test. The $48h-LD_{50s}$ of fipronil SC on honeybee were $0.005{\mu}g$ a.i./bee in acute contact toxicity test and $0.004{\mu}g$ a.i./bee in acute oral toxicity test, respectively. In toxicity of residues on foliage test, fipronil showed over 90% of mortality during 28days after treatment at recommended application rate. The $DT_{50}$ of dislodgeable foliar residue was 9 days. Finally, In small scale field test, fipronil showed similar toxicity in the residues on foliage test. It was concluded that fipronil has very high acute toxicity and long residual toxicity to honeybee. Therefore, fipronil is highly toxic to bees exposed to direct treatment or residues on blooming crops or weeds. Do not apply this product or allow it to drift to blooming crops or weeds if bees are visiting the treatment area. To protect honeybee and wild pollinators from outdoor use of fipronil, ultimately it should need to limit for only indoor use to prevent pollinators from unintentionally exposure of fipronil.