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.

The Tg.AC (v-Ha-ras) transgenic mouse: nature of the model.

The Tg.AC (v-Ha-ras) transgenic mouse model provides a reporter phenotype of skin papillomas in response to either genotoxic or nongenotoxic carcinogens. In common with the conventional bioassay, the Tg.AC model responds to known human carcinogens and does not respond to noncarcinogens. It also does not respond to most chemicals that are positive in conventional bioassays principally at sites of high spontaneous tumor incidence. The mechanism of response of the Tg.AC model is related to the structure and genomic position of the transgene and the induction of transgene expression through specific mediated interactions between the chemicals and target cells in the skin.

Tg.AC genetically altered mouse: assay working group overview of available data.

In a Government/Industry/Academic partnership to evaluate alternative approaches to carcinogenicity testing, 21 pharmaceutical agents representing a variety of chemical and pharmacological classes and possessing known human and or rodent carcinogenic potential were selected for study in several rodent models. The studies from this partnership project, coordinated by the International Life Sciences Institute, provide additional data to better understand the models' limitations and sensitivity in identifying carcinogens. The results of these alternative model studies were reviewed by members of Assay Working Groups (AWG) composed of scientists from government and industry with expertise in toxicology, genetics, statistics, and pathology. The Tg.AC genetically manipulated mouse was one of the models selected for this project based on previous studies indicating that Tg.AC mice seem to respond to topical application of either mutagenic or nonmutagenic carcinogens with papilloma formation at the site of application. This communication describes the results and AWG interpretations of studies conducted on 14 chemicals administered by the topical and oral (gavage and/or diet) routes to Tg.AC genetically manipulated mice. Cyclosporin A, an immunosuppresant human carcinogen, ethinyl estradiol and diethylstilbestrol (human hormone carcinogens) and clofibrate, an hepatocarcinogenic peroxisome proliferator in rodents, were considered clearly positive in the topical studies. In the oral studies, ethinyl estradiol and diethylstilbestrol were negative, cyclosporin was considered equivocal, and results were not available for the clofibrate study. Of the 3 genotoxic human carcinogens (phenacetin, melphalan, and cyclophosphamide), phenacetin was negative by both the topical and oral routes. Melphalan and cyclophosphamide are, respectively, direct and indirect DNA alkylating agents and topical administration of both caused equivocal responses. With the exception of clofibrate, Tg.AC mice did not exhibit tumor responses to the rodent carcinogens that were putative human noncarcinogens, (di(2-ethylhexyl) phthalate, methapyraline HCl, phenobarbital Na, reserpine, sulfamethoxazole or WY-14643, or the nongenotoxic, noncarcinogen, sulfisoxazole) regardless of route of administration. Based on the observed responses in these studies, it was concluded by the AWG that the Tg.AC model was not overly sensitive and possesses utility as an adjunct to the battery of toxicity studies used to establish human carcinogenic risk.

Dermal carcinogenicity in transgenic mice: effect of vehicle on responsiveness of hemizygous Tg.AC mice to phorbol 12-myristate 13-acetate (TPA).

The Tg.AC mouse is being evaluated for use in short-term carcinogenicity bioassays. Because the dermal test protocol necessitates dissolving test agents we determined the effects of several solvents on responsiveness of hemizygous mice to dermal applications of the classical skin tumor promoter. phorbol 12-myristate 13-acetate (TPA). Mice of both sexes received dermal applications of either acetone (negative control) or TPA in various vehicles [acetone, 100% methanol, 70% and 100% ethanol, DMSO and mixtures of acetone and ethanol (1:1), acetone and DMSO (4:1 and 1: 1). and acetone and olive oil (4:1)]. Negative control animals did not exhibit papillomas. When administered in acetone. ethanolic or methanolic vehicles TPA caused prompt and robust papillomatous responses. TPA was also tumorigenic in all nonalcoholic vehicles, except the acetone-olive oil mixture. Papilloma responses were generally delayed when TPA was applied in the nonalcoholic solvents but the distinction between TPA-dosed and negative control groups was unequivocal. These results show that choice of vehicle may affect the quantitative and qualitative nature of the response of Tg.AC mice to TPA, but 8 of 9 vehicles proved satisfactory for delivery of TPA.

Carcinogenicity studies on MTBE: critical review and interpretation.

Chronic inhalation of toxic concentrations of MTBE caused renal tubular cell neoplasms in male Fischer 344 rats and hepatocellular adenomas in female CD-1 mice. In Sprague-Dawley rats the oral administration of MTBE was associated with increased incidences of Leydig cell tumors and of lymphomas and leukemias (combined) in males and females, respectively. Neither lymphomas nor leukemias were individually increased in treated females. leydig cell tumors are common in rats and do not predict human responses to drugs and chemicals. Neither MTBE nor its metabolite, t-butyl alcohol, possess mutagenic potential and a second metabolite, formaldehyde, is mutagenic in vitro but in vivo results are equivocal. MTBE-induced neoplasms are most likely produced through a nongenetic mechanism which requires chronic exposure to toxic doses. Because of the intense odor (and taste) of MTBE, humans will not tolerate either air or water concentrations sufficient to produce the cytotoxic precursors required to promote cellular proliferation.

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.

Dichlorvos carcinogenicity: an assessment of the weight of experimental evidence.

After 30 years of experience with human exposure to dichlorvos (DDVP) in the home, workplace, and sickroom, the U.S. EPA has published its intent to revoke the food additive registration of this cholinesterase-inhibiting insecticide. The basis for the Agency action is the result of the National Toxicology Program (NTP) toxicology and carcinogenesis study of DDVP in rats and mice (NTP Technical Report No. 342, September 1989). In those experiments the NTP considered the result in the female mouse portion of the study to afford unequivocal evidence of carcinogenicity. The NTP considered the interpretations of the male and female rat and the male mouse studies to be less than clear. Despite the NTP interpretation, the EPA considers the male rat data (increased incidence of mononuclear cell leukemia) to be sufficient to warrant the regulatory change. The purpose of this report is to summarize a review of the interpretation of the NTP data and to assess the predictive validity of the results relative to potential human health impact. Critical review of experimental data indicates that the evidence for a carcinogenic effect of DDVP in animals is equivocal. Further, DDVP possess no in vivo mutagenic activity in mammalian assay systems and it bears no significant structural similarity to known carcinogens. Therefore, a weight-of-the-evidence analysis leads to the conclusion that DDVP poses neither mutagenic nor carcinogenic risks to humans exposed under normal conditions of use of foreseeable conditions of misuse.

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.

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)

Carbon monoxide and cardiovascular disease: an analysis of the weight of evidence.

The role, if any, of environmental tobacco smoke (ETS) in the causation and/or exacerbation of cardiovascular disease remains to be proven and defined. Earlier workers suggested that ETS-associated carbon monoxide, nicotine, and/or polyaromatic hydrocarbons may be causative factors. The purpose of this review was to assess the weight of evidence supporting a role for ambient carbon monoxide in the etiology of human ischemic cardiovascular disease. The findings show that there is scant clinical or experimental evidence to support a role for carbon monoxide in the causation of ischemic heart disease. Further, the results of field studies of relative air quality in nonsmoking and smoking homes, offices, and public places show that ETS contributes only minor and toxicologically insignificant increments in ambient carbon monoxide concentrations. These increments are variable and easily masked by other common carbon monoxide sources such as internal combustion engines and the burning of cooking and heating fuels. It is concluded that if ETS plays a role in the etiology of cardiovascular disease, it is most likely not mediated through carbon monoxide.

Toxicology and carcinogenesis studies of dietary titanium dioxide-coated mica in male and female Fischer 344 rats.

Male and female Fischer 344 rats were fed diets containing 0, 1.0, 2.0, or 5.0% titanium dioxide (TiO2) coated mica for up to 130 wk. This dosage regimen produced no consistent or biologically important changes in survival, body weight gains, hematologic or clinical chemistry parameters or histopathology. Under the conditions of this 130 wk feeding study there was no evidence that TiO2-coated mica produced either toxicologic or carcinogenic effects at dietary concentrations as high as 5.0%. The results suggest that dietary exposure to TiO2-coated mica does not pose a significant human health hazard.

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.

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.

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.

Transplantation studies of preputial gland and epithelial skin neoplasms derived from benzidine-based dye carcinogenicity assays in Fischer 344 male rats.

Neoplasms of preputial gland and skin were obtained from Fischer 344 male rats on lifetime drinking water studies of the benzidine congener 3,3'-dimethoxybenzidine, C.I. Direct Blue 15 or C.I. Acid Red 114, bisazobiphenyl dyes derived from 3,3'-dimethoxybenzidine and 3,3'-dimethylbenzidine. Portions of these well differentiated neoplasms were implanted into the left mammary fat pad of Fischer 344 male recipients. The rate of growth, presence of local invasion and distant metastases, and morphologic features were observed following 4 serial transplantations. All implants appeared early, grew rapidly, and were histomorphologically similar to the original neoplasms. Metastases from transplants were observed with both preputial gland and skin tumor lines in serial passages. The transplantation results confirm the malignant nature of these neoplasms.