• Title/Summary/Keyword: enterohepatic recirculation

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Griseofulvin-Phenobarbital Interaction(II) -Effects of Phenobarbital Pretreatment on Enterohepatic Recirculation of Griseofulvin in Rats- (그리세오풀린-페노바르비탈 상호작용(II) -Rat에 있어서 페노바르비탈 전처리가 그리세오풀빈의 장.간순환에 미치는 영향-)

  • Koh, Ik-Bae;Lee, Yong-Bok
    • Journal of Pharmaceutical Investigation
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    • v.17 no.1
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    • pp.15-21
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    • 1987
  • Effects of phenobarbital pretreatment on the pharmacokinetics of enterohepatic recirculating griseofulvin were investigated by comparing normal to bile duct cannulated rats and also the effects of enhanced endogeneous bile flow on the absorption of griseofulvin were studied by means of in situ recirculation method in phenobarbital-pretreated rats. Phenobarbital was administered orally for five days at the dose of 75 mg/kg/day. The influence of phenobarbital pretreatment on the absorption rate constant, area under the plasma concentration-time curve, maximum plasma concentration of orally administered griseofulvin was not found in bile duct cannulated rats. Decreased absorption clearance and apparent partition coefficient of griseofulvin in accordance with the amount of endogeneous bile juice seemed to be due to the decrease of thermodynamic activity of griseofulvin as bile forms the micelle with griseofulvin.

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Behavior of the insecticide imidacloprid in crucian carp (Carassius auratus L.) and its toxic effects on organs (살충제 imidacloprid의 붕어(Carassius auratus L.)중 행적 및 장기에 대한 독성)

  • Ihm, Yang-Bin;Kim, Chan-Sub;Lee, Hee-Dong;Kim, Dae-Kyu;Kyung, Kee-Sung
    • The Korean Journal of Pesticide Science
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    • v.10 no.4
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    • pp.289-295
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    • 2006
  • In order to elucidate the behavior of the insecticide imidacloprid (1-(6-chloro-3-pyridylmethyl)-N-nitroimidazolidin-2-ylideneamine) in crucian carp (Carassius auratus L.) and its effects on the internal organs of crucian carp, the crucian carps were exposed to [$^{14}C$]imidacloprid at a predicted environmental concentration of 0.064 mg/L for 4 days. Imidacloprid in water was absorbed into crucian carps to reach the maximum concentration at 2 days after exposure. Unknown major metabolite and imidacloprid urea, minor metabolite, were detected in test water. The amounts of the [$^{14}C$]imidacloprid and its metabolites absorbed in gall were much higher than those in the other parts, strongly suggesting that biliary excretion involving enterohepatic recirculation could be an import route for the elimination of imidacloprid absorbed in crucian carps. Meanwhile, no toxic effects of imidacloprid on liver and kidney as well as the genital organs such as testis and ovary were observed by microscopic inspection.

Distribution of the fungicide hexaconazole in internal organs of carp (Cyprinus carpio L.) (살균제 hexaconazole의 잉어(Cyprinus carpio L.) 장기 중 분포)

  • Lee, Eun-Young;Park, In-Young;Kim, Byung-Seok;Park, Yeon-Ki;You, Oh-Jong;Park, Kyung-Hun;Kim, Kyun;Kyung, Kee-Sung
    • The Korean Journal of Pesticide Science
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    • v.11 no.4
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    • pp.217-221
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    • 2007
  • In order to elucidate the behavior of the fungicide hexaconazole (1-(6-chloro-3-pyrldyhnethyl)N-nitroimidazolidin-2-ylideneamine) in carp (Cyprinus carpio L.), carps were exposed to [$^{14}C$]hexaconazole at a predicted environmental concentration (PEC) of 0.32 mg $L^{-1}$ for 4 days under static conditions. Hexaconazole in water was absorbed into carps to reach the maximum concentration 2 days after exposure. The amounts of the [$^{14}C$]hexaconazole and its metabolites absorbed in gall were much higher than those in the other organs and especially those in gall 2 days after exposure were 25 and 67 times higher than those in liver and kidney, respectively, strongly suggesting that biliary excretion involving enterohepatic recirculation could be an import route for the elimination of hexaconazole absorbed in carps.

Behavior of the herbicide metolachlor in carps (제초제 metolachlor의 잉어체내 행적)

  • Kyung, Kee-Sung;Kim, Jin-Wha;Lee, Byung-Moo;Oh, Byung-Youl;Jeong, Young-Ho;Lee, Jae-Koo
    • The Korean Journal of Pesticide Science
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    • v.3 no.2
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    • pp.54-59
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    • 1999
  • In order to investigate the behavior of the herbicide metolachlor [2-chloro-6'-ethyl-N-(2-methoxy-1-methylethyl)aceto-O-toluidide] in fish, carps (Cyprinus carpio L.) were exposed to the herbicide at $LC_{10}$(1.93 mg/L) for 4 days. Metolachlor dissolved in water was absorbed rapidly into carps to mark the maximum concentration 6 hours after exposure. The amounts of the $^{14}C$-metolachlor and its metabolites absorbed in gall were much higher than those in the other parts, strongly suggesting that biliary excretion involving enterohepatic recirculation could be an important route for the elimination of metolachlor. The $^{14}C$-radioactivity distributed into aqueous phase fraction in test water and in carp extract was increased in time-dependent manner. Extraction rate of $^{14}C$ absorbed in carp tissues was decreased remarkably up to 6 hours after exposure, suggesting that the possible polar metabolites of metolachlor were transformed into the conjugates to form non-extractable bound residues.

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Methylene Blue (메틸렌 블루)

  • You, Ji-Young
    • Journal of The Korean Society of Clinical Toxicology
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    • v.8 no.1
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    • pp.1-6
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    • 2010
  • Methylene blue is a very effective reducer of drug-induced methemoglobinemia. It has dose-dependent oxidation or reduction properties. In most cases, a dose of 1 to 2 mg/kg IV given over 5 minutes and immediately followed by a 15- to 30-mL fluid flush to minimize the local pain is both effective and relatively safe. The onset of action is quite rapid, and the effects are usually seen within 30 minutes. The dose may be repeated after 30 to 60 minutes and then every 2 to 4 hours as needed. The total dose should not exceed 7 mg/kg as a single dose or 15 mg/kg within 24 hours. Repeated treatment may be needed for treating compounds that have prolonged elimination or those compounds that undergo enterohepatic recirculation (e.g., dapsone). Methylene blue can cause dose-related toxicity. At high doses, methylene blue can also induce an acute hemolytic anemia and rebound methemoglobinemia. The reasons for treatment failure with methylene blue include ineffective GI decontamination, the existence of other forms of hemoglobin (e.g., sulfhemoglobin), a low or high dose of methylene blue and the toxicokinetics of some agents, such as aniline, benzocaine or dapsone.

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