• Title/Summary/Keyword: dissipation factor standard

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Dissipation Pattern of Boscalid in Cucumber under Greenhouse Condition (시설 내 오이 재배 중 살균제 Boscalid의 잔류특성)

  • Lee, Jong-Hwa;Park, Hee-Won;Keum, Young-Soo;Kwon, Chan-Hyeok;Lee, Young-Deuk;Kim, Jeong-Han
    • The Korean Journal of Pesticide Science
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    • v.12 no.1
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    • pp.67-73
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    • 2008
  • The dissipation patterns of a boscalid in cucumber under greenhouse condition was investigated to establish pre-harvest residue limit (PHRL) and biological half-life. Initial concentration of boscalid in cucumber at standard application rate was $7.29\;mg\;kg^{-1}$ and decreased to $0.04\;mg\;kg^{-1}$ after 15 days with half-life of 1.9 day, while the initial concentration was $14.69\;mg\;kg^{-1}$ and decreased to $0.11\;mg\;kg^{-1}$ after same period with half lift of 2.0 day at double application rate. PHRL was suggested by prediction curve derived from the decay curve of boscalid at double rate treatment. For example, $10.39\;mg\;kg^{-1}$ was calculated for 10 days before harvest, and $1.73\;mg\;kg^{-1}$ for 5 days. Dilution effect was major factor far the decrease of boscalid residue due to fast increasement of weight of cucumber during cultivation. Final residues level of boscalid was predicted based on the dissipation curve and guideline on safe use, when boscalid was used to control powdery mildew and gray mold. At standard rate application, $1.26\;mg\;kg^{-1}$ and $1.33\;mg\;kg^{-1}$ were calculated as final residue levels for control powdery mildew and gray mold, respectively, which are above the MRL(Meximum Residue Limit).

Prediction of the Minimum Required Pressure of Soundless Chemical Demolition Agents for Plain Concrete Demolition (무근콘크리트 해체시 무소음화학팽창제의 최소요구팽창압 예측)

  • Kim, Kyeongjin;Cho, Hwangki;Sohn, Dongwoo;Koo, Jaehyun;Lee, Jaeha
    • Journal of the Computational Structural Engineering Institute of Korea
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    • v.31 no.5
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    • pp.251-258
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    • 2018
  • In construction site, conventional methods such as jackhammer or explosive methods(dynamite) have been often used for the demolition of structures. Use of those methods are more carefully treated in environmentally and historically sensitive area. For those reasons, use of Soundless Chemical Demolition Agent(SCDA) is getting the spotlight. The SCDA is a powder which has expansive strength when it is mixed with water. In these Characteristics, SCDA can destroy the concrete or rock as it is poured into boreholes of the concrete or rock structures. However, there is no industrial standard for the use of SCDA effectively yet. In this study, experimental study to measure the expansive pressure was conducted depending on various boundary conditions such as waterproof, length of the steel pipe, submerged of steel pipe. Furthermore, computational analysis using damage plasticity model to predict the minimum required pressure of the SCDA for the concrete demolition depending on spacing between holes(k-factor) and compressive strength of the concrete was conducted. Obtained results indicates that water heat dissipation with submerged steel pipe shows the stable pressure for measuring the SCDA and hole distance(k-factor) is the most important factor for crack initiation of concrete.

Study of Pesticide Residue Allowed Standard of Methoxyfenozide and Novaluron on Aster scaber during Cultivation Stage (취나물에 사용하는 Methoxyfenozide 및 Novaluron의 생산단계 농약잔류허용기준 연구)

  • Hong, Ji-Hyung;Lim, Jong-Sung;Lee, Cho-Rong;Han, Kook-Tak;Lee, Yu-Ri;Lee, Kyu-Seung
    • The Korean Journal of Pesticide Science
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    • v.15 no.1
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    • pp.8-14
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    • 2011
  • Methoxyfenozide and novaluron was sprayed on Aster scaber during cultivation period. Samples were collected 7 times in 0-10 days after spraying. Both methoxyfenozide and novaluron were extracted with methanol, partitioned with dichloromethane and analyzed by HPLC. At the fortified level of 0.4 and $2\;mg{\cdot}kg^{-1}$, average recovery of methoxyfenozide were $102.5{\pm}3.03$ and $84.4{\pm}2.82%$, and novaluron were $88.7{\pm}2.32$ and $90.6{\pm}4.50%$, respectively. Biological half-life of methoxyfenozide was 3.99 days and novaluron which was 3.16 days at recommended spray level on cultivation period of the plant. The major reducing factor of novaluron was the increased weight of the plant. In case of application of methoxyfenozide and novaluron following pesticide guide line for safe use, the final residue level was calculated to lower than maximum residue level (MRL).