Phenolphthalein and bisacodyl: assessment of genotoxic and carcinogenic responses in heterozygous p53 (+/-) mice and syrian hamster embryo (SHE) assay.

Phenolphthalein (800 and 2400 mg/kg/day by gavage and 2400 mg/kg/day by diet) and bisacodyl (800-500, 4000-2000, and 8000 mg/kg/day by gavage) were administered to 15 male and 15 female and 20 male and 20 female p53(+/-) mice respectively for 26 weeks to investigate the potential carcinogenicity of each compound. Toxicokinetic analyses confirmed systemic exposure. p-Cresidine was administered by gavage (400 mg/kg/day) and served as the positive control agent in each study. Dietary phenolphthalein reduced survival in both sexes and early deaths were attributed to thymic lymphoma. No bisacodyl-related neoplasms were observed. Regardless of route of administration to p53(+/-) mice, phenolphthalein but not bisacodyl was unequivocally genotoxic, causing increased micronuclei in polychromatic erythrocytes. In the Syrian hamster embryo (SHE) cell transformation assay, phenolphthalein caused increases in morphologically transformed colonies, thereby corroborating NTP's earlier reports, showing phenolophthalein has potential carcinogenic activity. Bisacodyl was negative in the SHE assay. Results of these experiments confirm an earlier demonstration that dietary phenolphthalein causes thymic lymphoma in p53(+/-) mice and show that (1) phenolphthalein causes qualitatively identical results in this transgenic model regardless of route of oral administration, (2) phenolphthalein shows evidence of micronucleus induction in p53(+/-) mice for up to 26 weeks, (3) phenolphthalein induced transformations in the in vitro SHE assay, and (4) bisacodyl in p53(+/-) mice induces neither drug-related neoplasm, nor micronuclei in polychromatic erythrocytes, and did not induce transformations in the in vitro SHE assay.

ras gene activation in rat tumors induced by benzidine congeners and derived dyes.

Dimethoxybenzidine (DMO) and dimethylbenzidine (DM) are used to synthesize dyes such as C.I. Direct Blue 15 and C.I. Acid Red 114, respectively. These commercially used dyes are metabolically degraded to DMO or DM in the intestinal tract of rodents and subsequently DMO and DM are absorbed into the blood stream. Animals were exposed to DMO, DM, or the dyes in the drinking water. Tumors obtained from control and chemical-treated animals were examined for the presence of activated oncogenes by the NIH 3T3 DNA transfection assay. Activated oncogenes were detected in less than 3% (1/38) of the tumors from control animals whereas 68% (34/50) of the tumors from chemical-treated animals contained detectable oncogenes. Activated oncogenes were detected in both malignant (25/36) and benign (9/14) tumors from the chemically treated animals but only in one of 13 malignant tumors from the control animals. The presence of oncogenes in the chemically induced benign tumors suggests that oncogene activation was an early event in those tumors. Southern blot analysis of transfectant DNA showed that the transforming properties of the chemically induced rat tumor DNAs were due to the transfer of an activated H-ras (31/34) or N-ras (3/34) gene. One spontaneous rat tumor DNA was found to contain an activated H-ras gene. Oligonucleotide hybridization analysis indicated that the H-ras oncogenes from chemical-associated tumors contained mutations at codons 12, 13, or 61 whereas the spontaneously activated H-ras gene contained a point mutation at codon 61. These data suggest that activation of cellular ras genes by point mutation is an important step in the induction of tumors, at least in rats, by this class of benzidine-derived dyes. Moreover, in light of common histogenesis of the normal counterparts of many of the chemically induced neoplasms and histological evidence of varied tissue differentiation in some basal cell neoplasms, it is possible that most or all of the chemically induced neoplasms were derived from a common epidermal progenitor stem cell population.

Polybrominated dibenzo-p-dioxins and dibenzofurans: literature review and health assessment.

Polybrominated dibenzo-p-dioxins (PBDDs) and dibenzofurans (PBDFs) occur as trace (ppb) contaminants in brominated flame retardants and are produced during combustion of these chemicals. They are also formed when organics are incinerated in the presence of bromine, e.g., in municipal and industrial incinerators and in internal-combustion engines. Combustion of organics in the presence of both bromine and chlorine results in the formation of mixed (i.e., bromo, bromo/chloro and chloro) halogenated dibenzo-p-dioxins and dibenzofurans (HDDs and HDFs). There are 4600 potential mixed congeners. The biological effects of PBDDs and PBDFs are similar, if not identical, to those of PCDDs and PCDFs. Both groups of compounds induce hepatic aryl hydrocarbon hydroxylase (AHH) and ethoxyresorufin-o-deethylase (EROD) in rats and cause wasting and thymic atrophy in rats and guinea pigs. Tetrabrominated dinenzo-p-dioxin (TBDD) and dibenzofuran (TBDF) are reproductive toxins in mice and produce skin lesions in the rabbit-ear acnegenic test. The brominated compounds appear to bind to the same cytosolic receptors believed to mediate the toxicities of the chlorinated analogs. When compared on a molar-concentration basis, the brominated compounds are equipotent to the chlorinated analogs. TBDD is absorbed after oral, dermal, or intratracheal administration in rats, stored in the liver and adipose tissue, and eliminated in the feces through biliary excretion. The biological half-lives of the brominated compounds appear to be somewhat shorter than those of the corresponding chlorinated species. The brominated compounds, like their chlorinated congeners, have the potential to cause dermal, hepatic, and gastrointestinal toxicities in humans.(ABSTRACT TRUNCATED AT 250 WORDS)

Summary of the National Toxicology Program benzidine dye initiative.

The benzidine dye initiative is a research program established by the National Toxicology Program to generate an integrated body of scientific information regarding the potential health risks associated with exposure to benzidine- and benzidine-congener-derived dyes. Because an in-depth evaluation of each of the hundreds of benzidine-congener-derived dyes was considered impractical, the research program was designed to study the metabolism and disposition, genetic toxicity, and in vivo toxicity and carcinogenicity of two primary benzidine congeners, 3,3'-dimethylbenzidine and 3,3'-dimethoxybenzidine, and a select group of prototypical dyes derived from those amines. It was anticipated that by applying the basic information generated in these extensive studies, it would be possible to make regulatory decisions about other dyes after conducting only a minimal number of experiments such as studies of disposition and metabolism, and in vitro mutagenicity. This paper summarizes the results of studies conducted to evaluate the metabolism, disposition, mutagenicity, toxicity, and carcinogenicity of representative benzidine congeners and derived dyes.

Thirteen-week toxicity studies of 3,3'-dimethoxybenzidene and C.I. Direct Blue 15 in the Fischer 344 rat.

The benzidine congener 3,3'-dimethoxybenzidine (DMOB), and C.I. Direct Blue 15 (Blue 15), a prototypical compound of the DMOB-derived class of dyes, were evaluated in 13-week studies to characterize the toxicity and establish dose levels for subsequent chronic studies. Groups of 10 Fischer 344 rats of each sex were administered either DMOB, or Blue 15, at 1 of 5 concentrations in drinking water for 13 weeks. DMBO concentrations were 0, 0.017, 0.033, 0.063, 0.125, and 0.25% for males and females. For Blue 15, the concentrations were 0.063, 0.125, 0.25, 0.50, and 1.0% for females and 0, 0.125, 0.25, 0.50, 1.0, and 3.0% for male rats. Rats showed dose-related decreases in water consumption and weight gains. All DMOB-treated rats and their controls survived the 13-week treatment. There were 7 deaths in the 3% level of male rats treated with Blue 15. Liver and kidney weights were increased in rats treated with both compounds. Target organs for DMOB-treated rats were the kidney and thyroid. These lesions were characterized by chronic nephropathy, and increased pigment in the follicular cells of the thyroid. The kidney and liver were identified as target organs for Blue 15-treated rats. In the high-dose rats that died before termination of the study, renal effects were characterized by degeneration and focal necrosis of proximal tubular epithelial cells. Liver lesions in this group consisted of degeneration and necrosis of hepatocytes, fatty metamorphosis, and minimal megalocytosis. Mild chronic nephropathy was the principal histological effect in Blue 15-treated rats surviving to study termination.

Comparative carcinogenicity of two structurally similar phenylenediamine dyes (HC blue no. 1 and HC blue no. 2) in F344/N rats and B6C3F1 mice.

Toxicology and carcinogenesis studies of 2 structurally-related p-phenylenediamines, HC Blue No. 1, and HC Blue No. 2 were conducted by administering each chemical in feed for 103 weeks to both sexes of Fischer 344/N rats and B6C3F1 (C57BL/6N x C3H/HEN) mice. Diets containing 0, 1500, or 3000 ppm HC Blue 1 were fed to male and female rats and male mice; female mice received diets with 0, 3000, or 6000 ppm. Diets containing 0, 5000, or 10,000 ppm HC Blue 2 were fed to male rats and mice and the females received diets containing 0, 10,000 or 20,000 ppm. These concentrations were compatible with long-term growth and survival. The results demonstrated substantial differences in the neoplastic and non-neoplastic lesions caused by these structural analogs. HC Blue 2 caused histocytosis in lungs and hyperostosis of the skull in rats, and splenic hematopoiesis, fibrous osteodystrophy, and hyperostosis of the skull in mice. These non-neoplastic lesions were not observed in rats or mice treated with HC Blue 1. Contrasting, in male and female mice, HC Blue 1 produced dose-related increases in the incidences of both adenomas and carcinomas of the liver. HC Blue 1 produced a marginally positive trend in hepatocellular nodules and carcinomas in male rats and dose-related increases in hyperplasias and neoplasms of the lungs in female rats. In contrast, there was no evidence of carcinogenicity for HC Blue 2 in either sex of rats or mice, despite the fact that it was administered 3-5 times the dose of the HC Blue 1. Since these 2 nitroaromatic compounds differ only in the methyl vs. 2-hydroxyethyl substituent on the secondary amine of ring carbon 4, the great discordance in their carcinogenicity is most probably due to side group-directed alteration in their metabolic profiles.

14-day and 90-day toxicity studies of C.I. Pigment Red 3 in Fischer 344 rats and B6C3F1 mice.

Treatment of F344 rats and B6C3F1 mice with C.I. Pigment Red 3 in the diet (10, 5.0, 2.5, 1.25, 0.6 or 0.3%) for 14 and 90 days resulted in haematological alterations consistent with haemolytic anaemia. Rats appeared to be more sensitive than mice to the haematological effects. Histological lesions were observed in rats and mice after exposure for 90 days. Target organs in the rat were the spleen, bone marrow, liver and kidney. Lesions in the spleen consisted of a haematopoietic cell proliferation, iron-positive pigment and congestion of the red pulp, and inflammation of the splenic capsule. Changes in the livers of rats consisted of haematopoietic cell proliferation and iron-positive pigment in Kupffer cells. Haematopoietic cell proliferation also occurred in the bone marrow of treated rats. The presence of iron-positive pigment and a slightly increased incidence of protein casts were seen in the kidney. Target organs in mice were the spleen, liver and kidney. Histological lesions in mice after exposure for 90 days included increased haematopoietic cell proliferation in the liver and spleen, and iron-positive pigment in the spleen. Mild cytomegaly of the renal tubular epithelia was also observed in exposed mice.

Phospholipid degradation is induced by heat in alpha-tocopherol-enriched eggs.

A comparative study was undertaken to determine the effect of an alpha-tocopherol- and iodine-enriched laying diet on the phospholipid profile of egg yolk. In addition to the comparative study between the experimental and control eggs, experiments were conducted to determine the effects of heating on the phospholipid profile and the comparative molar ratios of cholesterol and total phospholipid. The phospholipid composition determined for frozen egg yolk samples showed no differences for the major components of phosphatidylcholine and phosphatidylethanolamine between the control and experimental diet group. In control eggs, exposure to boiling water produced time-related elevations in the concentration of lyso-phosphatidylcholine. A similar heat-related elevation in lyso-phosphatidylethanolamine was observed in both groups after 10 min. A time shift was observed in the heat susceptibilities of the experimental diet group. The control egg yolks hardened more quickly when exposed to heat. The results suggest protection against oxidative degradation of phospholipids and possible inhibition of phospholipases A2 and C, which may result from the elevated level of alpha-tocopherol in the experimental egg yolks.