RESUMO
This study compared the levels of cell proliferation and peroxisome proliferation in rodent liver with tumor incidence, to provide more information on the relationship between these events following chronic exposure. Fischer 344 rats were treated with 0, 100, 500, 2500, or 12,500 ppm DEHP, and B6C3F1 mice were treated with 0, 100, 500, 1500, or 6000 ppm DEHP in the diet for up to 104 weeks. Additional groups of rats and mice received the highest concentration for 78 weeks and then the control diet for an additional 26 weeks (recovery groups). Animals were terminated at weeks 79 and 105 for histopathologic examination. Elevated palmitoyl CoA oxidation activity and higher liver-to-body weight ratios were observed for the 2500- and 12,500-ppm groups of rats, and for the 500-, 1500-, and 6000-ppm groups of mice at Week 105. No increase in palmitoyl CoA oxidation activity was evident in the recovery group, and relative liver weights were near control levels following recovery. No hepatic cell proliferation was detected at Weeks 79 or 105 in either species although preliminary data indicated that cell proliferation did occur within the first 13 weeks of exposure. A significantly higher incidence of hepatocellular tumors was only observed for the 2500- and 12,500-ppm group and its recovery group of rats, and for the 500-, 1500-, and 6000-ppm groups and the recovery group of mice. The tumor incidences were reduced for the recovery groups compared with the groups fed DEHP continuously for 104 weeks. The data indicate that high levels of peroxisome proliferation and hepatomegaly are associated with DEHP hepatocarcinogenesis in rodent liver, and that the tumorigenic process may be arrested by cessation of DEHP treatment, suggesting that extended treatment with DEHP acts to promote tumor growth.
Assuntos
Carcinógenos/toxicidade , Dietilexilftalato/toxicidade , Hepatomegalia/induzido quimicamente , Neoplasias Hepáticas/induzido quimicamente , Transtornos Peroxissômicos/induzido quimicamente , Animais , Testes de Carcinogenicidade , Divisão Celular/efeitos dos fármacos , Relação Dose-Resposta a Droga , Feminino , Masculino , Camundongos , Tamanho do Órgão/efeitos dos fármacos , Oxirredução , Palmitoil Coenzima A/efeitos dos fármacos , Palmitoil Coenzima A/metabolismo , Proliferadores de Peroxissomos/toxicidade , Peroxissomos/enzimologia , Ratos , Ratos Endogâmicos F344 , Fatores Sexuais , Taxa de Sobrevida , Fatores de TempoRESUMO
The chlorinated acetic acids, in particular dichloroacetic acid (DCA), are found as chlorine disinfection by-products in finished drinking water supplies. DCA has previously been demonstrated to be a mouse liver carcinogen. Chronic studies are described in which male Fischer (F344) rats were exposed to DCA in their drinking water. In the first study, 28 day old rats were exposed to a regimen of 0.05, 0.5 and 5.0 g/l DCA. When animals in the high dose group began to exhibit peripheral hind leg neuropathy, the dose was lowered in stages to 1 g/l. These animals were sacrificed at 60 weeks due to the severe, irreversible neuropathy and were not included in this analysis. The remaining groups of animals were treated for 100 weeks. In the second study, rats were initially exposed to 2.5 g/l DCA which was lowered to 1 g/l after 18 weeks. The mean daily concentration (MDC) of 1.6 g/l was calculated over the 103 week exposure period. Time-weighted mean daily doses (MDD) based on measured water consumption were 3.6, 40.2 and 139 mg/kg bw/day for the 0.05, 0.5 and 1.6 g/l DCA respectively. Based upon the pathologic examination, DCA induced observable signs of toxicity in the nervous system, liver and myocardium. However, treatment related neoplastic lesions were observed only in the liver. A statistically significant increase of carcinogenicity (hepatocellular carcinoma) was noted at 1.6 g/l DCA. Exposure to 0.5 g/l DCA increased-hepatocellular neoplasia, (carcinoma and adenoma) at 100 weeks. These data demonstrate that DCA is an hepatocarcinogen to the male F344 rat. Calculation of the MDD at which 50% of the animals exhibited liver neoplasia indicated that the F344 male rat (approximately 10 mg/kg bw/day) is ten times more sensitive than the B6C3F1 male mouse (approximately 100 mg/kg bw/day). A "no observed effects level' (NOEL) of 0.05 g/l (3.6 mg/kg/day) was the same as for the mouse (3-8 mg/kg/day).
Assuntos
Ácido Dicloroacético/toxicidade , Administração Oral , Animais , Peso Corporal/efeitos dos fármacos , Testes de Carcinogenicidade , Ácido Dicloroacético/administração & dosagem , Ácido Dicloroacético/análise , Fígado/efeitos dos fármacos , Fígado/patologia , Neoplasias Hepáticas/induzido quimicamente , Masculino , Índice Mitótico/efeitos dos fármacos , Tamanho do Órgão/efeitos dos fármacos , Palmitoil Coenzima A/biossíntese , Palmitoil Coenzima A/efeitos dos fármacos , Ratos , Ratos Endogâmicos F344 , Abastecimento de ÁguaRESUMO
Data on the subchronic toxicity of 2-ethylhexanol (2EH) were required to establish the dose vehicle and dose levels for oncogenicity studies. In preliminary studies 2EH was given subacutely (11 days) to male and female Fischer 344 rats and B6C3F1 mice as an aqueous emulsion by oral gavage (0, 100, 330, 1000, and 1500 mg/kg/day). Clinical observations were made, body weights, food consumption, clinical chemistries, hematologies, and selected organ weights were measured, and gross and micropathologies were performed. Target organs were the central nervous system, liver, forestomach, spleen, thymus, and kidney in rats and the central nervous system, liver, and forestomach in mice. 2EH was then administered by oral gavage to male and female F344 rats and B6C3F1 mice as an aqueous emulsion (0, 25, 125, 250, and 500 mg/kg/day) for 13 weeks. At 500 mg/kg/day in the rat there was reduced body weight gain (6% male, 7% female), increased relative liver (29% male, 15% female), kidney (16% male, 6% female), stomach (11% male, 16% female), and testes (6%) weights, and moderate gross and microscopic changes in the liver and forestomach. There were no behavioral effects or effects on the spleen or thymus. A no-effect level for target organ effects in the rat was 125 mg of 2EH/kg/day. At 500 mg of 2EH/kg/day in the mouse the only effects were increased relative stomach weights in males (13%) and a low incidence of gross and microscopic findings in the forestomach (male and female) and liver (female). A no-effect level for target organ effects in the mouse was 125 mg of 2EH/kg/day. 2EH was a peroxisome proliferator in the rat but not in the mouse at subchronic dose levels of 500 mg/kg/day. Dose levels in oncogenicity studies were set at 50 mg/kg/day for the absence of treatment-related effects in rats and mice, and 500 and 750 mg/kg/day, respectively, in rats and mice as high doses producing minimal toxicity without altering the life span.