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Biomedical subjects

J K Dunnick

Publications and source records attributed to J K Dunnick.

At least 37 records · Page 2Linked to original sources

Tumors of the skin in the HRA/Skh mouse after treatment with 8-methoxypsoralen and UVA radiation.

8-Methoxypsoralen (8-MOP) with and without UVA radiation was administered to HRA/Skh mice (36 animals per treatment group) three times a week in the feed for a total dose of 9-80 mg/kg/week for 52 weeks. Most of the animals at the top dose of 8-MOP with UVA radiation had developed skin toxicity and/or skin tumors by 52 weeks. The skin lesions seen after treatment with 8-MOP and UVA radiation were characterized as squamous cell hyperplasia, squamous cell papilloma, and squamous cell carcinoma and are similar to what has been reported in humans after exposure to 8-MOP and UVA. Squamous cell hyperplasia and acute inflammation of the cornea were also seen in some of the treated female mice. Oral administration of 8-MOP and UVA did not result in a carcinogenic response to other organ systems. There were no increases in skin neoplasms after 8-MOP or UVA radiation alone. 8-MOP given in combination with UVA was carcinogenic to the skin of mice at dose levels similar to those used to treat psoriasis in humans.

Animals↗

Hematologic toxicity of AZT and ddC administered as single agents and in combination to rats and mice.

Toxicity studies of 3'-azido-2',3'-dideoxythymidine (AZT) and 2',3'-dideoxycytidine (ddC) were conducted in F344/N rats and B6C3F1 mice. The drugs were administered as single agents and in combination. In all studies, animals were treated by oral gavage twice a day, 7 days a week. In studies of the individual compounds, each was administered for 13 weeks at the following concentrations: AZT in rats, 0, 125, 250, 500, 1000 mg/kg and in mice, 0, 25, 50, 100, 400, 1000 mg/kg; ddC in rats and mice, 0, 250, 1000, 2000 mg/kg. Additional male rats and female mice that were treated with 0, 250, 1000, or 2000 mg/kg ddC and male and female mice treated with 0, 50, 400, 1000 mg/kg AZT were maintained for 30 days after treatment was stopped (at 94 days) to evaluate the reversibility of toxic effects. Hematologic variables were measured on Days 5, 23, and 94 (last day of dosing), and on Day 123 (after a 30-day period without treatment). AZT and ddC produced dose-related, poorly regenerative, macrocytic anemias as evidenced by decreases in erythrocyte counts, hematocrits, and hemoglobin concentrations and increases in mean corpuscular hemoglobin and mean corpuscular volume. Bone marrow samples in rats treated with AZT were hyperplastic whereas those in mice treated with AZT and rats and mice treated with ddC were hypoplastic. The hematologic toxicity of AZT was more severe than that of ddC. Generally, toxic effects of either chemical were greater in mice than in rats and more pronounced in female than in male animals. After 30 days without dosing, hematologic effects either resolved or dramatically improved. In studies in which ddC and AZT were administered in combination for 4 weeks at concentrations of 0/0, 0/500, 500/0, 10/500, 100/500, 500/500, and 500/1000 mg/kg ddC/AZT, there was macrocytic anemia in animals in the lower doses and marked microcytic anemia in surviving male mice in higher dose groups. Most female mice died in the 500/500 and 500/1000 mg/kg ddC/AZT dose groups. At lower concentrations (100/500, 500/1000 mg/kg ddC/AZT), effects of the two drugs were similar to those in the single drug studies. At higher concentrations (500/500 and 500/1000 mg/kg ddC/AZT), the combination treatment produced enhanced hematopoietic toxicity. These studies demonstrated the early and progressive time course of toxicity of AZT and ddC, species differences in sensitivities and responses, and reversibility of effects after termination of treatment. Based on these findings, a chronic toxicity study is being conducted with AZT in mice.

Animals↗

Decreases in spontaneous tumors in rats and mice after treatment with amphetamine.

Toxicology and carcinogenesis studies of dl-amphetamine sulfate, a drug used in the treatment of weight control, narcolepsy, and behavioral syndromes in children, were performed in F344/N rats and B6C3F1 mice. In these studies, amphetamine was administered for 2 years at doses of 0, 20, or 100 ppm in the feed to groups of 50 animals/dose/sex/species. The average amount of amphetamine consumed per day was estimated to be 1 or 5 mg/kg for low or high dose rats, 4 or 30 mg/kg for low or high dose male mice, and 3 or 19 mg/kg for low or high dose female mice. Survival was similar in dosed and control groups. The most notable effect of long-term treatment with this drug was the reduction of body weight in comparison to controls, and reduction in spontaneous tumors including pheochromocytomas of the adrenal gland in male rats, fibroadenomas of the mammary gland in female rats, adenomas of the anterior pituitary gland in male and female rats and female mice, endometrial stromal polyps of the uterus of female rats, adenomas or carcinomas of the liver in male and female mice, adenomas of the Harderian gland in male and female mice, and adenomas or carcinomas of the lung in male and female mice. Decreases in spontaneous tumors have previously been seen in 2-year rodent studies in groups of animals that have a reduced body weight in comparison to controls, but the spectrum of reduction in spontaneous neoplasms after treatment with amphetamine is broader than has previously been observed.

Adrenal Gland Neoplasms↗

Developmental toxicity of orally administered 2',3'-dideoxycytidine in mice.

2',3'-Dideoxycytidine (DDC), a potent inhibitor of human immunodeficiency virus (HIV), is presently undergoing clinical trials as a promising anti-AIDS drug. Since there are very limited published animal toxicity data available, and nucleoside analogues are being considered for treatment of HIV-infected pregnant women, a study was conducted in mice to investigate the potential adverse developmental effects of this drug. DDC, suspended in 0.5% methyl cellulose, was administered via gavage twice per day during gestation days (gd) 6 through 15 to C57Bl/6N mice in a total dose of 0, 200, 400, 1,000, or 2,000 mg/kg/day. Maternal weight gain during the gestation and treatment period, as well as gravid uterine weight, decreased significantly in the 2,000 mg group, but weight gain, corrected for gravid uterine weight, was not affected by DDC. The percent resorptions per litter increased significantly in the highest dose group, and there were fewer live litters because of complete litter resorption in six dams. Among litters with live fetuses, the mean litter size was significantly reduced in the 2,000 mg group. Average fetal body weight per litter decreased significantly in the 1,000 and 2,000 mg groups. The number of fetuses with any malformation, the number of litters with one or more malformed fetuses and the percent of malformed fetuses per litter increased significantly in the 1,000 and 2,000 mg groups. There was an increase in malformations at 400 mg/kg/day; however, it was not statistically significant. In conclusion, DDC produced developmental toxicity (malformations, reduced fetal body weight, and resorptions) in the absence of overt maternal toxicity except for body weight changes due to resorptions and reduced fetal weights.

Animals↗

The immunotoxicity of three nickel compounds following 13-week inhalation exposure in the mouse.

Groups of B6C3F1 mice were exposed to aerosols of nickel subsulfide (Ni3S2), nickel oxide (NiO), or nickel sulfate hexahydrate (NiSO4.6H2O) 6 hr/day, 5 days per week for 65 days to determine the immunotoxicity of these compounds. Exposure concentrations were 0.11, 0.45, and 1.8 mg Ni/m3 for Ni3S2, 0.47, 2.0, and 7.9 mg Ni/m3 for NiO; and 0.027, 0.11, and 0.45 mg Ni/m3 for NiSO4. Thymic weights were decreased only in mice exposed to 1.8 mg Ni/m3 Ni3S2. Increased numbers of lung-associated lymph nodes (LALN), but not spleen nucleated cells, were seen with all compounds. Nucleated cells in lavage samples were increased in mice exposed to the highest concentrations of NiSO4 and NiO and to 0.45 and 1.8 mg Ni/m3 Ni3S2. Increased antibody-forming cells (AFC) were seen in LALN of mice exposed to 2.0 and 7.9 mg Ni/m3 NiO and 1.8 mg Ni/m3 Ni3S2. Decreased AFC/10(6) spleen cells were observed in mice exposed to NiO, and decreased AFC/spleen were seen for mice exposed to 1.8 mg Ni/m3 Ni3S2. Only mice exposed to 1.8 mg Ni/m3 Ni3S2 had a decrease in mixed lymphocyte response. All concentrations of NiO resulted in decreases in alveolar macrophage phagocytic activity, as did 0.45 and 1.8 mg Ni/m3 Ni3S2. None of the nickel compounds affected the phagocytic activity of peritoneal macrophages. Only 1.8 mg Ni/m3 Ni3S2 caused a decrease in spleen natural killer cell activity. Results indicate that inhalation exposure of mice to nickel can result in varying effects on the immune system, depending on dose and physicochemical form of the nickel compound. These nickel-induced changes may contribute to significant immunodysfunction.

Aerosols↗

Thirteen-week toxicity study of n-hexane in B6C3F1 mice after inhalation exposure.

B6C3F1 mice were exposed to n-hexane 6 h/day, 5 days/week for 13 weeks at concentrations of 0, 500, 1000, 4000, and 10,000 ppm and at 1000 ppm 22 h/day, 5 days/week for 13 weeks (1000C group). Toxicological endpoints assessed included clinical signs, body and organ weight changes, gross and histopathology, neuropathology, and a battery of neurobehavioral tests. All mice survived the treatment. Exposure-related effects of n-hexane included sneezing at 10,000 ppm and body weight gain depression at 1000C and 10,000 ppm. Histopathologic changes included mild inflammatory, erosive and regenerative lesions in the olfactory and respiratory epithelium of the nasal cavity at 1000C, 4000, and 10,000 ppm. The only neurobehavioral parameter affected was a decrease in locomotor activity in female mice at 1000C and 10,000 ppm. In teased fiber preparations of tibial nerve, paranodal axonal swellings were observed at 1000C or at 10,000 ppm, but not in the control groups. The severity of the peripheral nerve lesion was mild. These studies show that n-hexane has minimal toxicity to the nervous system and respiratory system of mice.

Administration, Inhalation↗

Toxicity studies of amphetamine sulfate, ampicillin trihydrate, codeine, 8-methoxypsoralen, alpha-methyldopa, penicillin VK and propantheline bromide in rats and mice.

Thirteen-week toxicity studies in F344/N rats and B6C3F1 mice were conducted to determine general toxicity and target organ toxicity with amphetamine sulfate, ampicillin trihydrate, codeine, 8-methoxypsoralen, alpha-methyldopa sesquihydrate, penicillin VK, and propantheline bromide. This paper discusses the toxicity observed; use of the toxicity data to set dose levels for subsequent 2-year studies; and comparison of dose levels administered to rodents with doses used in the treatment of human disease. Drugs were administered orally in the feed or by gavage. The lowest doses in the 13-week studies were comparable to therapeutic doses in man on a mg/m2 (body surface area) basis or 5-10 times doses used in man on a mg/kg body weight basis. Little toxicity was seen at the low dose level with ampicillin, penicillin VK, 8-methoxypsoralen or propantheline bromide. At higher doses, target organ toxicity seen included the urinary bladder in male rats after propantheline bromide; the glandular stomach in rats and mice after penicillin VK; the liver and adrenals in rats after 8-methoxypsoralen; and the kidney in mice and rats after alpha-methyldopa. After amphetamine, codeine, or ampicillin administration, no target organ toxicity was seen in rats or mice, even at doses which caused body weight gain depression. The high doses chosen for subsequent 2-year studies were within 10 times human dose levels when compared on a mg/m2 body surface area.

Ampicillin↗

Kidney and urinary bladder lesions in F344/N rats and B6C3F1 mice after 13 weeks of 2,2-bis(bromomethyl)-1,3-propanediol administration.

Thirteen-week toxicity studies of the flame retardant 2,2-bis(bromomethyl)-1,3-propanediol (BMP; dibromoneopentyl glycol; FR-1138; CAS No. 329690-0) were conducted in male and female F344/N rats and B6C3F1 mice. The chemical was administered by oral gavage in corn oil 5 days per week for 13 weeks to rats at doses of 0, 50, 100, 200, 400, and 800 mg/kg and to mice at doses of 0, 25, 50, 100, 200, and 400 mg/kg, or in the feed for 13 weeks at concentrations of 0, 1250, 2500, 5000, 10,000, and 20,000 ppm for rats and at 0, 625, 1250, 2500, 5000, and 10,000 ppm for mice. There was a dose-related decrease in body weight gain in rats and mice after chemical administration. Mortality attributed to toxicity of BMP was seen in the gavage study in 2/10 high-dose (800 mg/kg) male rats and 3/10 high-dose (400 mg/kg) male mice no dose-related mortality occurred in the feed study. Minimal degeneration in the renal papilla was seen in male rats at 800 mg/kg in the gavage study and at doses of 5000 ppm or more in the feed study. This was also present in one female rat at the 20,000 ppm dose. In male mice renal papillary necrosis occurred at 400 mg/kg after dosing by the gavage route and at 2500, 5000, and 10,000 ppm in the dosed-feed study. In female mice papillary necrosis occurred only at the 10,000 ppm dose in the feed study. Tubular cell regeneration of the renal cortex was also present in mice at the same dose levels at which the papillary necrosis was observed. Transitional cell hypeplasia of the urinary bladder was seen in male rats at 400 and 800 mg/kg and in both sexes of mice at 200 and 400 mg/kg. Hyperplasia of the urinary bladder was also seen when BMP was administered in the feed at doses of 20,000 ppm to male rats; at doses of 2500, 5000, and 10,000 ppm to male mice; and at doses of 5000 and 10,000 ppm to female mice. The kidney and urinary bladder are target organs when BMP is administered by gavage or the dosed-feed route; mice were more sensitive than rats for the development of kidney and bladder lesions. Male rats and mice were more sensitive than females for the development of renal papillary degeneration or necrosis.

Animals↗

Lung toxicity after 13-week inhalation exposure to nickel oxide, nickel subsulfide, or nickel sulfate hexahydrate in F344/N rats and B6C3F1 mice.

The relative toxicity of nickel oxide (NiO), nickel sulfate hexahydrate (NiSO4.6H2O), and nickel subsulfide (Ni3S2) was studied in F344/N rats and B6C3F1 mice after inhalation exposure for 6 hr/day, 5 days/week, for 13 weeks. Exposure concentrations used (as mg Ni/m3) were 0.4-7.9 for NiO, 0.02-0.4 for NiSO4.6H2O, and 0.11-1.8 for Ni3S2. No exposure-related effects on mortality and only minor effects on body weight gain were seen in rats or mice. The most sensitive parameter for nickel toxicity was histopathologic change in the lungs of exposed animals were chronic active inflammation, fibrosis, and alveolar macrophage hyperplasia were associated with nickel exposure. There was an exposure-related increase in lung weight in rats and mice. Equilibrium levels of nickel in the lung were reached by 13 weeks of nickel sulfate and nickel subsulfide exposure, whereas lung levels of nickel continued to increase throughout exposure to nickel oxide. Additional exposure-related histopathologic lesions in treated animals included atrophy of the olfactory epithelium after nickel sulfate and nickel subsulfide exposure. No nasal lesions were seen after nickel oxide exposure. Lymphoid hyperplasia of the bronchial lymph nodes developed in animals exposed to all three nickel compounds. The order of toxicity corresponded to the water solubility of the nickel compounds, with nickel sulfate being most toxic, followed by nickel subsulfide and nickel oxide.

Administration, Inhalation↗

Two-year toxicity and carcinogenicity studies of ampicillin trihydrate and penicillin VK in rodents.

Toxicology and carcinogenesis studies of ampicillin trihydrate and penicillin VK, two widely used beta-lactam antibiotics, were performed in F344/N rats and B6C3F1 mice. In these studies ampicillin trihydrate was administered for 2 years to rats at doses of 0, 750, or 1500 mg/kg and to mice at doses of 0, 1500, or 3000 mg/kg, and penicillin VK was administered to rats and mice at doses of 0, 500, or 1000 mg/kg. Both drugs were administered by oral gavage in corn oil. Toxic lesions of the stomach were seen in rats and mice after ampicillin trihydrate administration and in mice after penicillin VK administration. In male rats that received ampicillin trihydrate there was a marginal increase in incidence of mononuclear cell leukemia and pheochromocytomas of the adrenal gland medulla. There was no evidence for carcinogenic activity in female rats or male and female mice after ampicillin trihydrate administration or in rats and mice after penicillin VK administration.

Ampicillin↗

Biochemical responses of rat and mouse lung to inhaled nickel compounds.

Nickel subsulfide (Ni3S2), nickel sulfate (NiSO4), and nickel oxide (NiO) are encountered occupationally in the nickel refining and electroplating industries, with inhalation being a common route of exposure. The purposes of this study were to evaluate the biochemical responses of lungs of rats and mice exposed for 13 weeks to occupationally relevant aerosol concentrations of Ni3S2, NiSO4, and NiO, to correlate biochemical responses with histopathologic changes, and to rank the compounds by toxicity. Biochemical responses were measured in bronchoalveolar lavage fluid (BALF) recovered from lungs of exposed animals. Parameters evaluated in BALF were lactate dehydrogenase (LDH), beta-glucuronidase (BG), and total protein (TP). Total and differential cell counts were performed on cells recovered in BALF. All compounds produced an increase in LDH, BG, TP, and total nucleated cells, and an influx of neutrophils, indicating the presence of a cytotoxic and inflammatory response in the lungs of exposed rats and mice. Increases in BG were greater than increases in LDH and TP for both rats and mice. Chronic active inflammation, macrophage hyperplasia, and interstitial phagocytic cell infiltrates were observed histologically in rats and mice exposed to all compounds. Statistically significant increases in BG, TP, neutrophils, and macrophages correlated well with the degree of chronic active inflammation. Results indicated a toxicity ranking of NiSO4 greater than Ni3S2 greater than NiO, based on toxicities of the compounds at equivalent mg Ni/m3 exposure concentrations.

Aerosols↗

Comparative inhalation toxicity of nickel sulfate to F344/N rats and B6C3F1 mice exposed for twelve days.

Groups of F344/N rats and B6C3F1 mice were exposed to aerosols of nickel sulfate hexahydrate (NiSO4.6H2O) 6 hr/day for 12 days to determine the short-term inhalation toxicity of this compound. Target exposure concentrations were 60, 30, 15, 7, 3.5, and 0 mg NiSO4.6H2O/m3. Endpoints evaluated included clinical signs, mortality, quantities of Ni in selected tissues, effect on mouse resistance to tumor cells, and pathological changes in tissues of both rats and mice. All mice exposed to 7 mg NiSO4.6H2O/m3 or greater and 10 rats exposed to 15 mg NiSO4.6H2O/m3 or greater died before the termination of exposures. Quantities of Ni remaining in lungs of rats at the end of the exposure were independent of exposure concentration. Lung burdens of Ni in mice were approximately one-half that in lungs of rats. Exposure of female mice to 3.5 mg NiSO4.6H2O/m3 had no effect on resistance to tumor cells as determined by spleen natural killer cell activity. Histopathological changes were seen in tissues of rats and mice exposed to as low as 3.5 mg NiSO4.6H2O/m3. Lesions related to NiSO4.6H2O exposure occurred in lung, nose, and bronchial and mediastinal lymph nodes. Results indicated that exposure of rats and mice to amounts of NiSO4.6H2O aerosols resulting in Ni exposure concentrations only eight times greater than the current threshold limit value for soluble Ni (0.1 mg/m3) for as little as 12 days can cause significant lesions of the respiratory tract.

Administration, Inhalation↗

Development of kidney tumors in the male F344/N rat after treatment with dimethyl methylphosphonate.

Dimethyl methylphosphonate (DMMP), a chemical that has been used as a flame retardant and as a nerve gas simulant to mimic the physical but not biologic properties of nerve gases, was administered by gavage in corn oil for up to 2 years at doses of 0, 500, or 1000 mg/kg/day to male and female F344/N rats and at doses of 0, 1000, or 2000 mg/kg/day to male and female B6C3F1 mice. Survival in dosed male rats was reduced, due in part to kidney toxicity, and lesions in the kidney included increased severity of spontaneous nephropathy, calcification, hyperplasia of the tubular and transitional epithelium, tubular cell adenocarcinomas, and transitional cell papillomas and carcinomas. Survival in female rats was similar among groups; survival in mice was reduced and this reduced survival decreased the sensitivity for detecting a carcinogenic response. There were no dose-related neoplastic responses in female rats or male or female mice. The spectrum of kidney lesions seen in the male rat given DMMP is similar to that seen after the long-term administration of a variety of other chemicals including unleaded gasoline, hydrocarbon solvents, and 1,4-dichlorobenzene.

Adenocarcinoma↗

Comparative toxicity of nickel oxide, nickel sulfate hexahydrate, and nickel subsulfide after 12 days of inhalation exposure to F344/N rats and B6C3F1 mice.

The relative toxicity of nickel oxide (NiO), nickel sulfate hexahydrate. (NiSO4.6H2O), and nickel subsulfide (Ni3S2) was studied in F344/N rats and B6C3F1 mice after inhalation exposure for 6 h/day, 5 days/week for 12 exposure days. Exposure concentrations used (as mg Ni/m3) were 0.9-23.6 for NiO; 0.8-13.3 for NiSO4.6H2O, and 0.4-7.3 for Ni3S2. For each compound there were 5 exposure groups plus a control group. NiSO4.6H2O was the most toxic compound with exposure related mortality seen at exposure concentrations of 13.3 mg/m3 in rats and 1.6 mg/m3 and above in mice. For Ni3S2, mortality was seen in mice (but not in rats) at the highest exposure concentration (7.3 mg/m3). No mortality was seen after NiO exposure. Lesions of the lung and nasal cavity were seen in both rats and mice after exposure to NiSO4.6H2O and Ni3S2 at the 4 highest exposure concentrations. Lesions of the lung were seen primarily at the highest exposure concentrations after NiO exposure. The amount of nickel in the lungs at the end of exposure varied in relation to the water solubility of the compounds. Based on these 2-week studies, the toxicity ranking was NiSO4.6H2O greater than Ni3S2 much greater than NiO. Additional studies are in progress to assess the relative toxicities of these three nickel compounds after 90-day exposures.

Administration, Inhalation↗

Respiratory tract lesions in F344/N rats and B6C3F1 mice after inhalation exposure to 1,2-epoxybutane.

1,2-Epoxybutane, a short-chain epoxide used as a stabilizer in chlorinated hydrocarbon solvents, was administered by inhalation exposure as a vapor 6 h/day, 5 day/week, for 24 months at exposure concentrations of 0, 200 or 400 ppm to F344/N rats and 0, 50, or 100 ppm to B6C3F1 mice. Survival of all groups of rats was 50% or greater until week 98 but was reduced in exposed groups by the end of the study. Survival in male mice was comparable among groups. Survival in female mice was greater than 50% until week 86, but was then reduced in the high-exposure group of mice. Exposure-related inflammatory, degenerative, and proliferative lesions occurred in the nasal cavity of both rats and mice. Seven papillary adenomas occurred in the nasal passages of high-exposure male rats and 2 in the nasal passages of high-exposure female rats. Alveolar/bronchiolar adenoma or carcinoma (combined) occurred with increased incidence in exposed male rats relative to controls. No exposure-related neoplastic lesions were seen in mice. After inhalation exposure, 1,2-epoxybutane was carcinogenic in rodents as were other epoxides or related compounds including propylene oxide, 1,3-butadiene, and ethylene oxide. The site of carcinogenic activity was considered to be related to length of the carbon chain.

Administration, Inhalation↗

Bromodichloromethane, a trihalomethane that produces neoplasms in rodents.

Bromodichloromethane, a trihalomethane found in water supplies after chlorination, was administered by gavage in corn oil to male and female F344/N rats and B6C3F1 mice for up to 2 years at dose levels of 0, 50, or 100 mg/kg to rats, 0, 25, or 50 mg/kg to male mice, and 0, 75, or 150 mg/kg to female mice. Survival at 2 years in rats and in male mice was comparable among groups and was greater than 50% at the termination of the experiment. Survival in female mice was greater than 50% in all groups until week 84 but was reduced toward the end of the study because of ovarian abscesses in some female mice. There was clear evidence of carcinogenicity in males and females of both species as shown by increased incidences of tubular cell adenomas and adenocarcinomas in the kidney and adenocarcinomas and adenomatous polyps in the large intestine in male and female rats, increased incidences of tubular cell adenomas and adenocarcinomas in the kidney of male mice, and increased incidences of hepatocellular adenomas and carcinomas in female mice. Of the three trihalomethanes studied to date in the National Cancer Institute/National Toxicology Program (chloroform, chlorodibromomethane, or bromodichloromethane) bromodichloromethane caused the widest spectrum of neoplasms in rodents.

Adenocarcinoma↗

Toxicity of 8-methoxypsoralen, 5-methoxypsoralen, 3-carbethoxypsoralen, or 5-methylisopsoralen with ultraviolet radiation in the hairless (HRA/Skh) mouse.

An experimental design to simulate PUVA therapy (oral 8-methoxypsoralen followed by uv radiation) has been tested in a 13-week subchronic study to determine the relative toxicities of 8-methoxypsoralen (8-MOP), 5-methoxypsoralen (5-MOP), 5-methylisopsoralen (5-MIP), and 3-carbethoxypsoralen (3-CEP) in inbred hairless mice (HRA/Skh). Drug was administered by 1-hr pulse feedings three times a week after mice were fasted overnight; individually housed animals were then exposed to uv radiation (320-400 nm; less than 2% output less than 320 nm). 8-MOP or 5-MOP administered orally (at doses of approximately 240 or 480 mg/m2 body surface area per week) followed one-half hour later with uv radiation of 2 J/cm2 for 13 weeks were found to cause skin toxicity including inflammation, hyperplasia, ulceration, and cellular atypia. Dose-related toxicity was not seen in other organ systems. Corresponding levels of 5-MIP or 3-CEP with uv radiation did not produce skin toxicity. These studies show that the psoralens with two potential DNA-binding sites (8-MOP and 5-MOP) were more toxic than psoralens with only one photoreactive site (5-MIP and 3-CEP).

5-Methoxypsoralen↗

Subchronic toxicity of propantheline bromide administered in the feed to Fischer 344/N rats and B6C3F1 mice.

Propantheline bromide, a drug used for the treatment of peptic ulcers, was studied in male and female Fischer 344/N rats and B6C3F1 mice for subchronic toxicity. The drug was administered in the feed for 13 weeks at 0, 220, 670, 2000, 6000, and 24,000 ppm in both species. Propantheline bromide caused a decrease in weight gain at 24,000 ppm in male and female rats and at 6000 and 24,000 ppm in male and female mice. All rats survived the treatment. The top dose of 24,000 ppm was fatal to mice. Clinical signs of toxicity (dilated pupils and decreased gastrointestinal emptying), similar to the atropine-like effects of propantheline bromide in man, were seen in male and female rats at 24,000 ppm. Hyperplasia of the transitional epithelium of the urinary bladder was seen in high-dose male rats at the end of 13 weeks.

Administration, Oral↗