Metabolism and excretion of dimethoate following ingestion of overtolerance peas and a bolus dose

Data to guide an exposure assessment were obtained by giving sugar peas containing overtolerance dimethoate residues (17 ppm; 8% oxon) and a bolus dose of dimethoate to a healthy adult male. The dimethoate tolerance on peas was and remains 2 ppm. Serial total urine samples were collected and analysed for dimethoate and its oxon, dimethylphosphate, dimethylphosphorothioate (DMTP) and dimethylphosphorodithioate. The dose of dimethoate administered was approx. 0.1 mg/kg body weight and produced no symptoms of toxicity. Dimethylphosphates appeared in the urine within 2 hr. The major metabolite (about 60%) was DMTP. Only traces (< 0.5%) of dimethoate and oxon were recovered from urine. Acetylcholinesterase inhibition was not observed although urinary metabolites were prominent, indicating that they are better indicators of acute exposure than cholinesterase inhibition. The results obtained using a bolus dose were virtually identical to those from the trial with overtolerance peas, and indicated that dimethoate is readily absorbed and its urinary metabolites are readily eliminated following exposures to low doses (0.1 mg/kg body weight).     

Absorption, disposition kinetics, and metabolic pathways of cyclohexene oxide in the male Fischer 344 rat and female B6C3F1 mouse

Cyclohexene oxide (CHO) is a monomer intermediate used in the synthesis of pesticides, pharmaceuticals, and perfumes. Although CHO has a variety of industrial uses where direct human exposure is possible, very little is known about its fate in the body. Therefore, the objectives of this study were to determine the absorption, distribution, metabolism, and excretion of cyclohexene oxide after oral, intravenous, and dermal exposure in male Fischer 344 rats and female B6C3F, mice. After intravenous administration of [14C]CHO (50 mg/kg), CHO was rapidly distributed, metabolized, and excreted into the urine. Plasma concentrations of CHO rapidly declined and were below the limit of detection within 60 min. Average (+/- SD) values for terminal disposition half-life, apparent volume of distribution at steady-state, and systemic body clearance were: 19.3 +/- 1.6 min; 0.44 +/- 0.08 liter/kg; and 31.3 +/- 0.5 ml/kg * min, respectively. After oral administration of [14C]CHO (10 and 100 mg/kg), it was found that 14C-equivalents were rapidly excreted in the urine of both species. At 48 hr, the majority of the dose (73-93%) was recovered in urine, whereas fecal elimination accounted for only 2-5% of the dose. At no time after oral administration was parent CHO detected in the blood. However, its primary metabolite cyclohexane-1,2-diol was present for different lengths of time depending on the dose. Four metabolites were detected and identified in mouse urine by MS: cyclohexane-1,2-diol; cyclohexane-1,2-diol-O-glucuronide; N-acetyl-S-(2-hydroxycyclohexyl)-L-cysteine; and cyclohexane-1,2-diol-O-sulfate. The sulfate conjugate was not present in rat urine. Topical application of [14C]CHO (60 mg/kg) provided poor absorption in both species. The majority of 14C-equivalents applied dermally were recovered from the charcoal skin trap (approximately 90% of the dose). Only 4% of the dose was absorbed, and the major route of elimination was via the urine. To evaluate the toxicity of CHO, animals were given daily doses of CHO orally and topically for 28 days. No statistically significant changes in final body weights or relative organ weights were noted in rats or mice treated orally with CHO up to 100 mg/kg or up to 60 mg/kg when given topically. Very few lesions were found at necropsy, and none were considered compound related. In conclusion, regardless of route, CHO is rapidly eliminated and excreted into the urine. Furthermore, after either oral or dermal administration, it is unlikely that CHO reaches the systemic circulation intact due to its rapid metabolism, and is therefore unable to cause toxicity in the whole animal under the test conditions used in this study.     

In vivo proliferation of oligodendrocyte progenitors expressing PDGFalphaR during early remyelination

2,4-Pentanedione (2,4-PD; CAS No. 123-54-6), an industrial chemical, was investigated for its comparative pharmacokinetics in male Fischer 344 rats by a single intravenous (i.v.) injection of (4.3, 43, 148.5, and 430 mg/kg), or a 6-hr nose-only inhalation exposure (400 ppm) to 14C-2,4-PD. For the i.v. route, the plasma concentration of 14C-2,4-PD-derived radioactivity declined in a biexponential fashion. The overall form of the 14C plasma concentration-time curves and derived pharmacokinetic parameters indicated that dose-linear kinetics occurred in the i.v. dose range 4.3-148.5 mg/kg, but not with 430 mg/kg. Metabolism of 2,4-PD was quite rapid as the concentration of unmetabolized 2,4-PD declined steadily to undetectable after 8 hr. 14C-2,4-PD derived radioactivity was eliminated mainly as 14CO2 and in urine. For the 4.3, 43 and 148.5 mg/kg doses 14CO2 elimination was relatively constant (36.8, 38.8 and 42.3% in 48 hr samples respectively) and greater than urinary excretion (17.9, 14.3 and 29.6%; 48 hr specimens). At 430 mg/kg i.v. there was a reversal of the excretion pattern, with urine 14C excretion (54.7%) becoming greater than that for 14CO2 (27.3%). Excretion in expired volatiles and feces was small. Radiochromatograms of urine showed free 2,4-PD in the 12 hr sample, together with 7 other metabolites. Free 2,4-PD and 6 of the metabolites decreased or were not detectable in a 24 or 48 hr urine sample, but one peak (retention 7.9 min) increased progressively to become the major fraction (97%). Nose-only exposure to 400 ppm 14C-2, 4-PD produced a mean decrease in breathing rate of 20.1%, which was constant and sustained throughout exposure, due to a lengthening of the expiratory phase of the respiratory cycle. 14C-2,4-PD was rapidly absorbed during the first 3 hr of exposure, then began to plateau, but did not reach a steady state. Postexposure elimination of 14C from plasma followed a biexponential form with a t1/2 for the terminal disposition phase of 30.72 hr. Plasma unmetabolized 2,4-PD was present throughout the whole of the exposure phase, but was significantly less than total 14C. Postexposure, plasma unmetabolized 2,4-PD declined rapidly to undetectable concentrations by 12 hr. Radiolabel excretion was approximately equivalent in urine (37.6%) and expired 14CO2 (36.3%). Urine radiochromatograms showed a minor 2,4-PD contaminant (0.6-5.9% over 48 hr), along with 7 other peaks probably representing metabolites. As with the 148.5 mg/kg i.v. dose, the major metabolite peak was at 7.8 min retention, increasing from 41.1% (12 hr) to 62.8% (48 hr). Immediately postexposure, radioactivity was present in all tissues examined, but on a concentration basis (microgram equiv/g) there was no preferential accumulation of 14C in any tissue or organ. On a total organ basis, highest contents were in liver and kidney, presumably related to the metabolism and excretion of 2,4-PD. By 48 hr postexposure, concentrations had decreased in all tissues except fat, presumably due to the lipophilicity of 14C residues. The profile of the plasma-time radioactivity curves, and the presence of residual radioactivity in tissues at 48 hr postexposure, suggests that a cumulative process could occur with frequent repeated exposures.     

Human herpesvirus-8 glycoprotein B interacts with Epstein-Barr virus (EBV) glycoprotein 110 but fails to complement the infectivity of EBV mutants

ortho-Phenylphenol (OPP), a fungicide and antibacterial agent with food residues, is carcinogenic to rat bladder. The present studies provide information on changes in urinary composition and urinary metabolites, urothelial cytotoxicity and regenerative hyperplasia, and DNA adducts in male F344 rats fed OPP. An initial experiment evaluated dietary doses of 0, 1,000, 4,000, and 12,500 ppm OPP fed for 13 weeks. There was no evidence of urinary calculi, microcrystalluria, or calcium phosphate-containing precipitate, but urothelial cytotoxicity and hyperplasia occurred at the highest dose only. In a second experiment, rats were fed dietary OPP levels of 0, 800, 4,000, 8,000, and 12,500 ppm. Urinary pH was > 7 in all groups. Urinary volume was increased at the 2 highest doses with consequent decreases in osmolality, creatinine, and other solutes. Total urinary OPP metabolite excretions were increased, mostly excreted as conjugates of OPP and of phenylhydroquinone. Free OPP or free metabolites accounted for less than 2% excreted in the urine without a dose response. Urothelial toxicity and hyperplasia occurred only at doses of 8,000 and 12,500 ppm. OPP-DNA adducts were not detected in the urothelium at any dose. In summary, OPP produces cytotoxicity and proliferation of the urothelium at dietary doses > or = 8,000 ppm without formation of urinary solids. The paucity of unconjugated metabolites and the lack of OPP-DNA adducts suggests that OPP is acting as a bladder carcinogen in male rats by inducing cytotoxicity and hyperplasia without it or its metabolites directly binding to DNA.     

Isolation and identification of major urinary metabolites of rifabutin in rats and humans

The antimycobacterial drug rifabutin is extensively metabolized in humans and laboratory animals. About 40% of the dose is excreted in urine as unchanged drug, and lipophilic (extractable with 1-chlorobutane) and polar metabolites. Polar metabolites accounted for 59.1 +/- 2.5% and 88.8 +/- 4.4% of radioactivity in urine collected over 96 hr after intravenous administration of 25 and 1 mg/kg of [14C]rifabutin to Sprague-Dawley rats, respectively. After 48 hr, all urinary radioactivity consisted of polar metabolites. The most abundant polar metabolite, identified by electrospray ionization-MS, collision-induced dissociation-MS, and comparison of HPLC retention times with the synthetic standard, was N-isobutyl-4-hydroxy-piperidine. Lipophilic metabolites accounted for <20% of urinary radioactivity. Major lipophilic metabolites, 25-O-deacetyl-rifabutin, 27-O-demethyl-rifabutin, 31-hydroxy-rifabutin, 32-hydroxy-rifabutin, and 20-hydroxy-rifabutin were isolated from both human and rat urine by HPLC and identified by electrospray ionization-MS, collision-induced dissociation-MS, and NMR spectrometry. In addition, two metabolites formed by the oxidation of the N-isobutyl-piperidyl group of rifabutin were found in the urine of rats, but not humans.     

Pharmacokinetics and metabolic disposition of 14C-metronidazole-derived radioactivity in rat after intravenous and intravaginal administration

Urinary metabolites and the pharmacokinetics of radioactivity derived from 14C-metronidazole (14C-MTZ) were determined after intravenous (iv) or intravaginal (ivg) administration of 10 mg/kg to adult rats. Following iv or ivg administration, the disappearance of 14C from blood followed the kinetics of a two-compartment open-system model. The blood half-lives of 14C during the beta-phase were 10.9 +/- 1.6 and 13.6 +/- 4.2 hr, after iv and ivg administration, respectively. After ivg application, the MTZ-derived radioactivity was detected in tail blood at 5 min, peaked at 1 hr, declined rapidly to 6 hr and more slowly thereafter. The vaginal absorption half-life of 14C-MTZ was 0.28 +/- 0.09 hr. About 12% of the administered dose remained in the vagina after 1 hr and 1.5% after 24 hr. At 24 hr, the tissue distribution and concentration of 14C were similar in iv and ivg dosed rats, the highest 14C concentration being present in the kidneys and lowest in the fat. The percentages of the dose excreted in 24 hr in the urine and feces were 58 and 15 after iv administration, compared to 37 and 40 after the ivg route, respectively. Unchanged 14C-MTZ and five of its metabolites were detected in the urine irrespective of the route of administration. The results show that metronidazole is rapidly absorbed through the vaginal mucosa of the rat and the metabolism and excretion of this chemotherapeutic agent are influenced by the route of administration.     

Formic acid excretion in rats exposed to trichloroethylene: a possible explanation for renal toxicity in long-term studies

Rats exposed to trichloroethylene, either by gavage or by inhalation, excreted large amounts of formic acid in urine which was accompanied by a change in urinary pH, increased excretion of ammonia, and slight increases in the excretion of calcium. Following a single 6-h exposure to 500 ppm trichloroethylene, the excretion of formic acid was comparable to that seen after a 500 mg/kg dose of formic acid itself, yet the half-life was markedly different. Formate excretion in trichloroethylene treated rats reached a maximum on day 2 and had a half-life of 4-5 days, whereas urinary excretion was complete within 24 h following a single dose of formic acid itself. Formic acid was shown not to be a metabolite of trichloroethylene. When rats were exposed to 250 or 500 ppm trichloroethylene, 6 h/day, for 28 days, the only significant effects were increased formic acid and ammonia excretion, and a change in urinary pH. There was no evidence of morphological liver or kidney damage. Long-term exposure to formic acid is known to cause kidney damage suggesting that excretion of this acid may contribute to the kidney damage seen in the long-term studies with trichloroethylene.     

In vivo dexamethasone effects on neutrophil effector functions in a rat model of acute lung injury

1. In healthy male volunteers, the absorption, metabolite profiles and excretion of 14C-benidipine hydrochloride, a new Ca antagonist, were investigated after oral administration at a dose of 8 mg. 2. 14C-benidipine hydrochloride was rapidly absorbed, and the plasma concentration of radioactivity and unchanged drug reached a maximum of 71.2 ng eq./ml at 1.1 h and 2.56 ng/ml at 0.6 h respectively, and then declined bi-exponentially. The half-life in the elimination phase was 14.7 and 5.3 h respectively, AUC of unchanged drug was low, about 1% of that of radioactivity. 3. Five days after administration, 36.4% of the administered radioactivity was excreted in urine and 58.9% in faeces. 4. The metabolite profiles in plasma, urine and faeces were analysed by hplc. At 1 h after administration the predominant metabolites in plasma were M9 and M2, which accounted for 13.8 and 8.2% of the radioactivity respectively, whereas unchanged drug represented 1.2%. Predominant metabolites in urine 12 h after administration were M3 and M8, which accounted for 2.22 and 2.21% of the administered radioactivity respectively. Metabolites excreted in faeces 120 h after administration were very complex and poorly separated by hplc and could not be characterized: unchanged drug was not detected in the faeces.     

Negligible excretion of unchanged ketoprofen, naproxen, and probenecid in urine

On the average, 0.6% of a dose of ketoprofen or naproxen or 1.2% of a dose of probenecid was found in the urine of normal male volunteers assayed immediately after its collection. Between approximately 60 and 85% of the dose of these drugs can be excreted in the urine as conjugates, which rapidly hydrolyze at body temperature, at room temperature, and even during frozen storage, thereby regenerating the parent drug. Since urine collections involved sample retention in the bladder at 37 degrees for collection intervals as long as 2--3 hr, the given percentages excreted unchanged probably are overestimates. It is possible that no unchanged ketoprofen, naproxen, or probenecid is excreted in urine. This study contrasts with previous reports of up to 50% of a dose of ketoprofen and 15--17% of doses of naproxen and probenecid being excreted in urine as the parent compound. Those reports probably reflect primarily the duration of frozen sample storage between collection and assay along with the urine collection schedules employed the speed of the clinical procedures, and the analytical procedures used. Attention should be given to potential conjugate hydrolysis whenever the pharmacokinetics of carboxylic acids are studied.     

Taurine conjugation of 2,4-dichlorophenoxyacetic acid and phenylacetic acid in two marine species

1. At least 50% of a dose of 14C-labelled 2,4-dichlorophenoxyacetic acid or phenylacetic acid was excreted in urine in 48 hours after administration to dogfish shark or flounder. 2. For both compounds, more than 90% of the urinary 14C was present as a single metabolite. 3. Each metabolite was the taurine conjugate of the administered compound.     

Toxicity and metabolism in mice of 2,6-dithiopurine, a potential chemopreventive agent

2,6-Dithiopurine (DTP) has been proposed as a possible chemopreventive agent because of its facile reaction with the electrophilic ultimate carcinogen, benzo[a]pyrene diol epoxide, and other reactive electrophiles. Previous studies in mouse skin indicated almost complete inhibition of benzo[a]pyrene diol epoxide-induced tumorigenesis by DTP, suggesting the possible utility of this compound as a chemopreventive agent. However, little is known of the metabolism of DTP or of its possible long-term toxicity. Mice were fed diets containing up to 4% DTP in AIN-76A for a period of 7 weeks, and possible toxicity was monitored by weight gain and histopathological examination of all major tissues. No toxicity was observed at any dose of DTP. DTP was found to be a good substrate in vitro for two enzymes known to metabolize 6-mercapto-purine: xanthine oxidase and thiopurine methyltransferase. The in vitro metabolites were 2,6-dithiouric acid and an apparent monomethylated derivative, respectively. In vivo, the major urinary metabolite was 2,6-dithiouric acid, which attained levels as high as 34 mM in the urine of mice receiving the 4% DTP diet. DTP was also excreted unchanged in the feces and urine. DTP, 2,6-dithiouric acid, and an unidentified, relatively nonpolar metabolite were also detected in the serum of experimental animals. Although large interindividual variation in the serum DTP concentration was found, there was a dose-dependent increase in serum DTP as the dietary level of DTP was increased. These results suggest that neither toxicity nor metabolism will severely limit the utility of DTP as a chemopreventive agent.     

Metabolism and disposition of 14C-granisetron in rat, dog and man after intravenous and oral dosing

1. The disposition and metabolic fate of 14C-granisetron, a novel 5-HT3 antagonist, was studied in rat, dog, and male human volunteers after intravenous and oral administration. 2. Complete absorption occurred from the gastrointestinal tract following oral dosing, but bioavailability was reduced by first-pass metabolism in all three species. 3. There were no sex-specific differences observed in radiometabolite patterns in rat or dog and there was no appreciable change in disposition with dose between 0.25 and 5 mg/kg in rat and 0.25 and 10 mg/kg in dog. Additionally, there were no large differences in disposition associated with route of administration in rat, dog and man. 4. In rat and dog, 35-41% of the dose was excreted in urine and 52-62% in faeces, via the bile. Metabolites were largely present as glucuronide and sulphate conjugates, together with numerous minor polar metabolites. In man, about 60% of dosed radioactivity was excreted in urine and 36% in faeces after both intravenous and oral dosing. Unchanged granisetron was only excreted in urine (5-25% of dose). 5. The major metabolites were isolated and identified by MS spectroscopy and nmr. In rat, the dominant routes of biotransformation after both intravenous and oral dosing were 5-hydroxylation and N1-demethylation, followed by the formation of conjugates which were the major metabolites in urine, bile and plasma. In dog and man the major metabolite was 7-hydroxy-granisetron, with lesser quantities of the 6,7-dihydrodiol and/or their conjugates.     

Pharmacokinetics of single intravenous and oral doses of dolasetron mesylate in healthy elderly volunteers

Dolasetron mesylate (MDL 73,147EF, Anzemet; Hoechst Marion Roussel, Laval, Canada) is a 5-HT3 receptor antagonist undergoing clinical evaluation for use as an antiemetic agent. The pharmacokinetics of dolasetron and its reduced metabolite (MDL 74,156) were studied after administration of single intravenous and oral doses of dolasetron mesylate 2.4 mg/kg in 18 healthy elderly subjects. Expressed as the dolasetron base, this dose was 1.8 mg/kg. Dolasetron was rapidly metabolized to the reduced metabolite, which appeared in plasma within 10 minutes after intravenous or oral administration. The mean half-life (t1/2) of dolasetron was 0.24 hours after intravenous administration and 0.50 hours after oral administration. The pharmacokinetic parameters of the reduced metabolite were similar after intravenous and oral administration. The apparent absolute bioavailability of the reduced metabolite was 89%, and it had an elimination t1/2 of approximately 7 hours and an apparent volume of distribution (Vd beta) of 4.69 L/kg. Dolasetron was not detected in urine. Metabolites were excreted in urine almost completely within 24 hours of administration. The primary metabolite detected in urine was the (+)-enantiomer of the reduced metabolite, which accounted for 25.35% (+/- 7.79%) and 18.88% (+/- 7.65%) of the intravenous and oral doses, respectively. Hydroxylated metabolites accounted for 5% or less of the total dose via either route. The pharmacokinetics of the reduced metabolite after single intravenous or oral doses in elderly volunteers were consistent with pharmacokinetics observed in both young healthy men and cancer patients receiving high-dose cisplatin chemotherapy. Dosage adjustments of dolasetron mesylate on the basis of age do not appear to be necessary.     

Hair analysis for drugs of abuse. VI. The excretion of methoxyphenamine and methamphetamine into beards of human subjects

The excretion of methoxyphenamine (MOP) and methamphetamine (MA) into beards has been studied. Six healthy male subjects orally took 50 mg of MOP at a single dose and 7 doses for a successive 7 days. Their beard hairs were collected by an electric shaver every morning until MOP disappeared from the beard. After washing with 0.1% SDS, the beard samples were extracted with methanol-5 N HCl (20:1) under ultra-sonication for 1 h and the solution was kept overnight. MOP in the extract was determined by GC/MS using deuterium labelled MOP as an internal standard after trifluoroacetyl-derivatization. The drug concentrations in beard and the reproducibility of analysis were compared with the three procedures, unwashed, 0.1% SDS (wash I) and the additional ethanol (wash II) wash. The drug concentration in beard after SDS wash was 0.5-2.5 ng/mg lower than that in unwashed beard during the first 5-6 days. The drug concentration in beard after ethanol wash was much lower than that in the unwashed beard. The drug excreted into beard was detected 10 approximately 12 days for a single dose and 12-14 days for 7 doses after the last dosage at the cut off level of 1 ng/mg. On the contrary, the drug excreted in urine was not detected after more than 3 days after use. O-Desmethyl MOP, a major metabolite of MOP, was also detected in beard. The procedures were applied to the detection of MA in beard of MA abusers. It was realized that a beard sample was more useful than a urine sample assuming a longer detection.     

Absorption, pharmacokinetics and metabolism of 14C-sumatriptan following intranasal administration to the rat

1. Studies have been carried out to investigate the absorption of sumatriptan after intranasal administration to rats. The pharmacokinetics, metabolism and excretion of 14C-sumatriptan were compared following intranasal and intravenous dosing to male and female albino rats using an aqueous buffered formulation at pH 5.5. 2. Following intravenous administration sumatriptan was eliminated from plasma with a half-life of about 1.1 h. After intranasal administration there was rapid absorption of part of the dose and two peak plasma concentrations were observed, initially at 0.5 and then at 1.5-2 h. The elimination half-life after the second peak was estimated as being about 4 h. 3. Radioactivity was largely excreted in urine (up to 89% of dose in 168 h) after both intravenous and intranasal administration, with a faster rate of excretion after intravenous dosage (73% males, 64% females within 6 h) than after intranasal dosage (37% males, 40% females within 6 h). 4. 14C-sumatriptan was the major component in urine and in extracts of faeces after both intravenous and intranasal administration. The major metabolite excreted in urine and faeces was GR49336, the indole acetic acid analogue. 5. The results of this in vivo rat study suggest that absorption of the dose via the nasal mucosa is incomplete after intranasal administration and that there is a secondary absorption phase probably reflecting oral absorption of part of the dose. The bioavailability is estimated as about 30%, for the period 0-6 h.     

Chronic toxicity, oncogenicity, and mutagenicity studies with chlorotetrafluoroethane (HCFC-124)

The chronic toxicity, oncogenicity, and mutagenicity of chlorotetrafluoroethane (HCFC-124) were evaluated. In the chronic toxicity/oncogenicity study, male and female rats were exposed to 0, 2000, 10,000, or 50,000 ppm HCFC-124 for 6 hr/day, 5 days/week, for 2 years. Body weights were obtained weekly during the first three months of the study and every other week for the remainder of the study. Food consumption was determined weekly. Clinical signs of toxicity were monitored throughout the study. An ophthalmological examination was performed on all animals prior to study start, and all surviving rats were examined at approximately 3, 12, and 24 months after study start. Clinical pathology was evaluated at 3, 6, 12, 18, and 24 months. An interim termination was conducted at 12 months. All surviving rats were necropsied at 24 months. A complete set of tissues was collected for microscopic examination, and selected tissues were weighed. There were no compound-related, adverse effects on body weight, food consumption, survival, clinical signs of toxicity, ophthalmoscopically observable ocular lesions, serum hormone concentrations, or clinical pathology parameters at any exposure concentration in either male or female rats. Compared to controls, urine fluoride was increased in males and females at all exposure concentrations, and plasma fluoride was increased in females at all exposure concentrations. Excretion of fluoride represents conversion of the parent molecule, and as such is not considered to be an adverse effect. There were no toxicologically significant, compound-related organ weight changes or gross or microscopic findings in male or female rats at any of the exposure concentrations tested. HCFC-124 was not toxic or carcinogenic in rats of either sex after inhalation exposure at concentrations of up to 50,000 ppm in this two-year chronic toxicity/oncogenicity study. After exposure to HCFC-124 for six hours per day, five days per week, for 24 months, the no-observed-adverse-effect level for male and female rats was 50,000 ppm. HCFC-124 was not mutagenic in Salmonella typhimurium strains TA1535, TA97, TA98, and TA100 with and without activation when evaluated at concentrations up to 60% HCFC-124 for 48 hours. No evidence of clastogenic activity was observed in cultured human lymphocytes at atmospheric concentrations up to 100% HCFC-124 for 3 hours, with and without metabolic activation. In vivo, no micronuclei were induced in mouse bone marrow cells following exposure of mice to concentrations of 99,000 ppm HCFC-124 6 hours/day for 2 days.     

Percutaneous penetration and metabolism of topical (14C)flutamide in men

This study was designed to determine the fate of the nonsteroid antiandrogen flutamide in men following a single 6-hr topical application of 5 mg 14C-labeled drug dissolved in 50% ethanol/50% propylene glycol. Analysis of 0-120 hr urine shows at least 16% of the applied flutamide is absorbed. Fifty-six percent of the dose is recovered from the site of application with cotton swabs moistened with 50% ethanol/50% propylene glycol. Flutamide plasma levels peak in 4 to 6 hr at about 1.3 ng/ml and then decline rapidly to about 0.08 ng/ml 24 hr after application. Only 13% of plasma 14C is associated with flutamide 6 hr after drug application. There are at least 10 plasma metabolites, of which 6 have been tentatively identified. These are alpha, alpha, alpha-trifluoro-4'-amino-m-acetotoluidide (A); alpha, alpha, alpha-trifluoro-4'-amino-2-methyl-m-lactotoluidide (B); alpha, alpha, alpha-trifluoro-4'-nitro-m-acetotoluidide (C); alpha, alpha, alpha-trifluoro-2-methyl-4'-nitro-m-lactotoluidide (D); alpha, alpha, alpha-trifluoro-4'-amino-2-methyl-m-propionotoluidide (E); and alpha, alpha, alpha-trifluoro-6-nitro-m-toluidine (F). (D) is the major plasma metabolite, and its concentration exceeds flutamide's between 8 and 24 hr after drug. All the plasma metabolites are found in 0-24 hr urine in minor amounts. An additional metabolite, alpha, alpha, alpha-trifluoro-amino-5-nitro-p-cresol (G), accounts for 27% of urine 14C.     

Physiologically based pharmacokinetics and the dermal absorption of 2-butoxyethanol vapor by humans

It has generally been assumed that the skin contributes only minor amounts to the total uptake of solvent vapors, relative to the respiratory tract. Contrary to this assumption, the widely used glycol ether solvent, 2-butoxyethanol (BE), has been reported to be more effectively absorbed through the skin (75% of the total uptake) than through the lungs of humans (Johanson and Boman, 1991, Br. J. Ind. Med. 48, 788). The possibility that the finger prick blood sampling technique used in the Johanson and Boman study was confounded by locally high concentrations of BE at the site of absorption was suggested using a previously developed PBPK model (Corley et al., 1994, Toxicol. Appl. Pharmacol. 129, 61). The current study was conducted to verify the PBPK analysis and to determine whether or not the skin was the major site for absorption of BE vapor by exposing one arm from each of six human volunteers to 50 ppm 13C2-BE vapor for 2 hr. To evaluate the potential consequences of blood sampling techniques, samples were taken from both the unexposed arm (catheter; during and after exposure) and the exposed arm (finger prick; end of the exposure only) for analysis of both BE and its major metabolite, butoxyacetic acid (BAA). Butoxyacetic acid is responsible for the hemolysis observed in toxicity studies with laboratory animals. Humans, however, are significantly less sensitive to this effect. The concentration of BE in the finger prick blood samples averaged 1500 times higher than the corresponding concentration in venous blood sampled from a catheter installed in the unexposed arm at the end of the exposure. Blood BAA levels were generally within a factor of 4 of each other for the two techniques and, therefore, was considered a better indicator of systemic absorption. Urine was collected for 24 hr and analyzed for the following metabolites found in rat metabolism studies: free and conjugated BE, BAA, ethylene glycol (EG), and glycolic acid (GA), with only BAA detected in the human urine. More importantly, urinary BAA was found to be extensively conjugated ( approximately 67%) with glutamine, confirming recent reports. These results, coupled with PBPK modeling of worst-case exposure scenarios (no clothing, 100% of the body was exposed), demonstrated that no more than 15-27% (low-to-high relative temperatures and humidities), not 75%, of the total uptake of BE could be attributed to the skin of humans during simulated 8-hr exposures to the ACGIH TLV concentration of 25 ppm. Even less of the total uptake was attributed to the skin during simulations of exercise with whole-body exposures (5-9%) or by more realistic exposures of only the arms and head (1-8%). As a result, humans are unlikely to reach hemolytic concentrations of the metabolite BAA in blood following vapor exposures to BE.     

Effects of DDT in Fundulus: studies on toxicity, fate, and reproduction

The toxicity, absorption, distribution, metabolism, and effects on reproduction of DDT was studied using the killifish (Fundulus heteroclitus), a species of economic importance because of its widespread abundance and its presence toward the lower end of the food chain. 14C-DDT was administered by exposure from the ambient water. There was a rapid removal of the radioactive pesticide from the water accompanied by uptake of radioactivity primarily by carcass (primarily muscle tissue) and eggs of the fish. Most (greater than 92%) of the radioactivity in the carcass was shown by TLC methods to be the parent pesticide. One day after a single 24-hr exposure to 14C-DDT, approximately 70% of the administered radioactivity was found in the carcass and the levels of the tissue decayed with a t 1/2 of three days. One day after a single 24-hr exposure to 0.1 ppm of 14C-DDT, the organs that contained the highest concentration of the pesticide (ca. 5 ppm) were intestine and liver. When the pesticide was administered by two 24-hr exposures from water, the intestine, liver and ovaries contained the major concentration of radioactivity (7 to 14 ppm). Untreated Fundulus contained less than 0.2 ppm of total DDT-like compounds. A variety of doses and schedules were tested in an effort to maximize the absorption of DDT, while minimizing the mortality to the fish. An intermittent schedule of 24 hr in 0.1 ppm DDT followed by 24 hr in DDT-free sea water, repeated two times, was found to be optimal. At the levels examined, DDT delayed the rate of normal development of fertilized eggs from Fundulus, but did not appear to cause any observable alterations in the hatched fry. Fertilization of Fundulus eggs was significantly diminished when insemination was carried out in DDT-containing sea water.     

Radioimmunoassay of thyrotropin releasing hormone in plasma and urine

A sensitive and specific radioimmunoassay has been developed capable of measuring thyrotropin releasing hormone (TRH) in extracted human plasma and urine. All of three TRH analogues tested had little cross-reactivity to antibody. Luteinizing hormone releasing hormone, lysine vasopressin, rat growth hormone and bovine albumin were without effect, but rat hypothalamic extract produced a displacement curve which was parallel to that obtained with the synthetic TRH. Sensitivity of the radioimmunoassay was 4 pg per tube with intraassay coefficient of variation of 6.2-9.7%. Synthetic TRH could be quantitatively extracted by methanol when added to human plasma in concentration of 25, 50 and 100 pg/ml. TRH immunoreactivity was rapidly reduced in plasma at 20 degrees C than at 0 degrees C, but addition of peptidase inhibitors, FOY-007 and BAL, prevented the inactivation of TRH for 3 hr at 0 degrees C. The TRH in urine was more stable at 0 degrees C than 20 degrees C, and recovered 75 +/- 4.6% hr after being added. The plasma levels of TRH were 19 pg/ml or less in normal adults and no sex difference was observed. The rate of disappearance of TRH administered i.v. from the blood could be represented as half-times of 4-12 min. Between 5.3-12.3% of the injected dose was excreted into urine within 1 hr as an immunoreactive TRH. These results indicate the usefulness of TRH radioimmunoassay for clinical investigation.