• Current Research on Agriculture and Life Sciences
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• v.31 no.4
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• pp.272-279
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• 2013

The dissipation patters of the triazole fungicides flusilazole and myclobutanil in apples were investigated to establish the biological half-lives and pre-harvest residue limits (PHRLs). The residual amounts of the fungicides sprayed with single or triple doses were below the maximum residue limits (MRL) for apples established by Ministry of Food and Drug Safety. The dissipation constants of the fungicides in the apples were 0.0513 for flusilazole and 0.0244 for myclobutanil meaning their biological half-lives were calculated as 6.2-6.7 days for flusilazole and 13.3-24.8 days for myclobutanil. The PHRLs calculated using the dissipation constants indicated that the residual amounts of flusilazole and myclobutanil in the apples at the harvesting date would be below the MRLs if their residual amounts were 0.43 and 0.59 mg/kg, respectively, at 7 days prior to harvesting the apples.

• Journal of Food Hygiene and Safety
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• v.25 no.2
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• pp.91-99
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• 2010

Two pesticides commonly used in spinach were subjected to a field residue trial to ensure safety of terminal residues in the harvest. The residual patterns of two pesticides, which were Azoxystrobin and chlorpyrifos were examined after applying with the recommended dose and their $DT_{50}$ were calculated. Also degradation patterns of pesticides at storage $4^{\circ}C$ were compared to those at $20^{\circ}C$, and removal rates of pesticides by washing spinach with water were measured. Biological half-lives of azoxystrobin and chlorpyrifos were 3.2~3.8 and 3.8~4.7 days, respectively. During the storage period, the degradation patterns were appeared more obviously at $20^{\circ}C$ than $4^{\circ}C$. Removal rates of azoxystrobin and chlorpyrifos were 9.6~90.0% and 17.7~85.8% by various washing methods.

• Applied Biological Chemistry
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• v.43 no.4
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• pp.291-297
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• 2000

This study was conducted to find out the environmental factors affecting the differences in the half-life of the insecticide cyfluthrin in soil between field and laboratory tests carried out in 1998. Degradation and leaching of cyfluthrin in soil were examined under various environmental conditions that were considered to affect the residuality. Cyfluthrin was degraded 1.9 times faster in non-sterilized soil than in sterilized soil and 1.2 times at $25^{\circ}C$ than at $15^{\circ}C$. The half-lives of cyfluthrin were 61.4 days under the dark condition and 4.5 days under sunlight, and those were 11.8 days under the open condition and 23.8 days under the closed condition. The half-lives of the authentic compound and the commercial product of cyfluthrin were 15 and 1 day in the field test and 26 and 3 days in the laboratory test, respectively. Cyfluthrin was rapidly degraded with an increase in soil moisture content and decomposed faster in the alkaline solution of pH 12 than in the acidic solution of pH 3, but the half-life of cyfluthrin did not make any difference between pH 6.4 of the field test soil and pH 5.6 of the laboratory test soil. Cyfluthrin was immobile in soil from the results that $81{\sim}94%$ of the initial amount remained in the $0{\sim}2\;cm$ layer of the soil column regardless of the amount and time of rainfall after the chemical treatments. From viewing the abovementioned results, soil moisture content, sunlight and formulation type affected greatly soil microbes and volatilization affected slightly, and temperature, pH and rainfall did not affect the big difference in the half-life of cyfluthrin in soil between the field and laboratory tests in the year of 1998.

• Proceedings of the Korean Society of Applied Pharmacology
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• 1993.04a
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• pp.93-93
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• 1993

도파민 D 수용체 및 5-HT 수용체 차단기전을 지닌 새로운 항정신분열증 약물인 risperidone은 활성형 대사물로 9-OH risperidone을 체내에서 생성하는 바, 이 대사과정의 유전적 다형성의 여부 즉 hydroxylation 과정에 CYPIID6의 관여 여부를 검토코자 하였다. Metoprolol 100 mg 경구투여로 CYPIID6의 대사능의 표현형을 결정한 12명의 정상 피험자(11명: extensive metabolizer, 1명: poor metabolizer)를 대상으로 하였으며, 피험자는 risperidone 1 또는 2 mg 경구투여후 혈중 risperidone 및 9-OH risperidone 농도를 경시적으로 radioimmunoassay법으로 측정하였다. 이들 피험자중 6명의 extensive metabolizer는 quinidine 600 mg/day의 용량 투여로 CYPIID6의 활성도를 완전 억제시킨 후 risperidone 1 mg 경구투여에 따른 약동학적 성상을 재검토하여 risperidone hydroxylation에 CYPIID6의 관여 여부를 검토하였다. 1) 1명의 poor metabolizer는 extensive metabolizer에 비해 현저히 긴 risperidone 반감기를 보였다. 2) 12명의 피험자에서 관찰된 metoprolol metabolic ratio는 risperidone 혈장 반감기 및 log(risperidone AUC/9-OH-risperidone AUC)와 유의한 상관성을 나타내었다. 3) Quinidine 투여는 risperidone의 반감기의 유의한 증가와 9OH risperidone AUC의 현저한 감소를 보였으나, 9-hydroxylation 대사과정이 완전히 억제되지는 않았다.

• Analytical Science and Technology
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• v.15 no.1
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• pp.67-71
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• 2002

The residual analysis and half-life time of imidazole fungicide prochloraz in soils (silty clay) were investigated by gas chromatography equipped electron capture detector (GC-ECD). The soil samples were extracted acetone/hexane(1:1) solvent and analyzed after separated by $LC-NH_2$ Sep-Pak solid column. Linear sensitivity of standard calibration curve was Y = 268.8600X + 0.0664, $R^2=0.9998$ between 0.05~1.00 ng. The detection limit was 0.02 mg/L and the average recoveries were 94.5~97.3% from the standard additional experiments with 0.10 and 0.40 mg/L. The half-life time was 24.4 days in room laboratory and 7.6 days in the field test soil.

• Proceedings of the Korean Society of Applied Pharmacology
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• 1993.04a
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• pp.130-130
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• 1993

실험목적: KR 53170 및 KR 53234 는 천연물에서 분리 추출한 화합물로 terpene lacton ring을 가진 약산성 물질이다. in vitro 항종양 실험에서 종양억제효과가 있었고 in vivo 항종양 실험에서도 유의성 있는 효과가 있었으며 급성 경구독성시험에서도 독성이 낮은 것으로 평가 되었다. 이에 따라 KR 53170 등의 약물동태학적인 성질을 연구하여 독성실험과 임상실험을 위한 용법용량을 결정하고 나아가 본약물의 제제개발에 도움이 되도록 본 연구를 시행하였다. 방법: KR 53170 및 53234은 경구시 20mg/kg, 정맥투여시는 10mg/kg로 투여하였다. Rat의 혈장 sample 채취는 ether로 흡입마취 시킨 후 heart puncture 하였다. 뇨시료는 대사 cage를 이용하여 채취하였으며 얻어진 모든 시료는 HPLC로 분석 하였다. 분석결과는 computer program 'Multi-free'를 이용하여 주요 pqarameter를 산출하였다. 인체혈액에 대한 혈청단백결합율 측정은 ultrafiltration법을 이용하였다. 즉 YMT membrane을 이용하여주요 parameter를 산출하였다. 인체혈액에 대한 혈청단백결합율 측정은 ultrafiltration법을 이용하였다. 즉 YMT membrane을 이용하여 유리약물을 분리하여 HPLC로 정량하였다. 결과 및 고찰: 1. KR 53170 10mg/kg 정맥투여시 최고혈중농도는 0.55ug/ml, 반감기는 0.51hr, 분포용적은 4.5L이었다. 20mg/kg를 경구 투여시 최고 혈중농도는 0.18ug/ml, 반감기는 3.5기산이고 AUC는 0.91ug.ml, 분포용적 28Lm, Ka 3.49$hr^{－1}$ 그리고 Cl는 5.5L/hr/kg이었다. 이는 투여용량에 비해 매우 적은량이 흡수되고 배설 된 것으로 약물이 혈액에 대한 용해도 문제에 기인하는 것으로 간주된다. 2. KR 53234 10mg/kg 정맥투여후의 최고혈중농도는 1.14ug/ml, 반감기는 0.50hr, 분포용적은 2.2L이었다. 20mg/kg 경구 투여시의 최소 혈중 농도는 0.33 ug/ml, 소실반감기는 1.5시간, AUC는 0.942ug.hr/ml, 분포용적 11L, Ka는 3.05 $hr^{－1}$ 그리고 Cl는 5.3L/hr/kg이었다. 이는 KR 53170에서와 같이 매우 적은량이 흡수되고 배설되었다. 3. KR 53170의 혈청단백 결합율은 5-500 ug/ml 범위에서 78.7-86.2%이었고 KR 53234의 혈청단백결합율은 5-100 ug/ml 범위에서 79.6-71.2%이었다.이었다.

• Agrochemical news magazine
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• v.22 no.6 s.169
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• pp.28-29
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• 2001

• The Korean Journal of Pesticide Science
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• v.14 no.4
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• pp.332-338
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• 2010

Degradation characteristics of insecticide diazinon in upland and paddy soils under laboratory conditions were investigated to elucidate the effect of raw pig slurry (RPS) and processed pig slurry (PPS) treatment. Soil (20g) was treated with RPS and PPS by standard rate, double rate and triple rate before treating with diazinon (0.5mg/kg level) and incubating at ($25{\pm}2^{\circ}C$) for 60 days. The half-lives of diazinon in the untreated upland and paddy soil were about 28 and 22 days respectively. The degradation rate of diazinon was faster by $5.0{\pm}1.2$ days in the paddy soil than in the upland soil independent of fertilizer types. This result indicates that soil moisture content affects the half-life of diazinon probably by hydrolysis. Degradation of diazinon was faster in RPS treatment soil than in PPS treatment soil. The more amount of fertilizers were treated, the more rapidly diazinon degraded regardless of fertilizers and soil types. Based on the results obtained, degradation of diazinon in soil was definitely influenced by soil water contents and treatment of those fertilizers.

• Analytical Science and Technology
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• v.13 no.1
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• pp.34-40
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• 2000

The optimum conditions for the half-life time and residual analysis of the iminoactadine triacetate fungicide on soils were investigated by using the gas chromatography. Iminoctadine triacetate(IOTA) was extracted from soils with 2.0 M-NaOH/methanol and chloroform. The extracted IOTA was derivatized to pyrimidine hexafluroacetylacetone by the acetylation and analyzed with GC/ECD after elimination of moisture and impurities on the Sep-Pak column. From the standard addition experiments with 0.1 and 1.0 ppm, the average recoveries were ranged from 83.8 to 93.2 % and the detection limit was 0.005 ppm. The half-life time of iminoctadine triacetate in the silty clay was 30 days in the laboratory and 19.5 days in the field test whereas it was 27 days and 17.5 days for each in case of silty loam.

• Proceedings of the Korean Radioactive Waste Society Conference
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• 2009.06a
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• pp.401-402
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• 2009