Food and Chemical Toxicology

Light alcohol consumption was reported to be negatively associated with insulin resistance and risk of cardiovascular diseases; however, the results were inconsistent. We here investigate whether long term intake of low-concentration ethanol can affect adiponectin levels. Male Wistar rats were exposed to 0.1% ethanol in drinking water for 26 weeks. Visceral adipose tissue (VAT) was cultured and treated with ethanol, SB203580, GW9662, or rosiglitazone. Adiponectin in serum and culture supernatant were measured by ELISA, mRNA levels of adiponectin and PPARγ were determined by RT-PCR, and protein expressions of PPARγ, p38 MAPK and phospho-p38 MAPK were determined by Western blot. In vivo, ethanol decreased the mRNA of adiponectin in VAT and serum adiponectin significantly Decreased PPARγ and increased activation of p38 MAPK were observed in ethanol treated group. In vitro, SB203580 increased the adiponectin and PPARγ levels in normal DMEM cultured VAT and ameliorated ethanol-induced decrease of adiponectin and PPARγ expressions. GW9662 also decreased the adiponectin levels; Both ethanol and GW9662 weakened the rosiglitazone-induced elevation of adiponectin levels in cultured VAT. These data suggest that long term intake of 0.1% ethanol down-regulated adiponectin levels, and the regulation of PPARγ via p38 MAPK pathway plays an important role in the mechanism underneath.

Furan is commonly found in foods such as coffee, canned and jarred foods, including baby food containing meat, and various vegetables. It is thought to be formed by the thermal decomposition of carbohydrates. Furan is carcinogenic in rodents, although the detailed mechanism of action has not been completely established, for all the tumour types induced. Dose-response modelling of the data for hepatocellular tumours gives a BMDL10 of 1.23 mg/kg/day, and MOEs of between 750 and 4300 for exposures of infants and adults.

D-003 is a mixture of long-chain fatty acids isolated and purified from sugar cane wax, the major component of which is 1-octacosanoic acid and which possesses effective antiplatelet, antithrombotic and cholesterol-lowering effects. D-003 was suspended in 1% acacia gum solution, and given daily by gavage to rats at dose levels of 5, 100 and 1000 mg/kg/day on days 6 through 15 of gestation. Cyclophosphamide, serving as a positive control, was given at the dose of 50 mg/kg/day on day 15 of gestation. Evidence of maternal or developmental toxicity was not observed in the groups treated with D-003. Maternal clinical signs of toxicity were not observed and the analysis of initial body weight and the body weight gain during the treatment period was comparable among the groups treated with D-003 and control. As expected, cyclophosphamide caused both embryotoxic and teratogenic effects in rats. Meanwhile, no adverse effects on reproductive performance, or on embryonic or fetal development, including visceral and skeletal examination, were seen in any of the groups administered D-003. It is concluded that D-003 administered up to 1000 mg/kg/day did not induce any evidence of developmental toxicity.

D-003 is a mixture of long-chain fatty acids isolated and purified from sugar cane wax with cholesterol-lowering properties. D-003 given orally (500 and 1000 mg/kg/day) to female rats for 15 days prior to mating, through mating and gestation to day 21 of lactation and male rats for 4 weeks prior and during mating did not induce toxic effects on reproduction. There were no significant reductions in the number of animals that conceived, in the numbers of pups born to those that did conceive, in the numbers of pups that survived until weaning, and in their body weights at weaning. Drug-treated and control groups' offspring were comparable in growth, physical and behavioral development, spontaneous activity and reproductive performance. Pregnant New Zealand rabbits were given D-003 as oral doses of 500 and 1000 mg/kg/day on days 6 through 18 of gestation without any evidence of embryotoxicity or teratogenicity. The no-observed-effect dose in these two experimental studies was 1000 mg/kg/day. After assessment of the potential of high doses of D-003 to act on developing embryo and reproduction process, no evidence supports the conclusion that D-003 is a reproductive and developmental toxicant/teratogen.

D-003 is a mixture of high molecular weight sugarcane wax aliphatic primary acids with cholesterol-lowering, anti-platelet and antioxidant effects. This study investigated the long-term oral toxicity and carcinogenicity of D-003 in Sprague Dawley rats of both sexes, randomly distributed into four groups: a control group, treated only with the vehicle, and three treated with D-003 (50, 500 and 1500 mg/kg). All treatments were given orally for 24 months. Mortality (survival analysis), clinical symptoms, weight gain, food consumption, organ weights, time-to-tumour or tumour incidence data were not shown between group differences or trends. With the exception of serum cholesterol levels, lower in D-003-treated groups (500 and 1500 mg/kg) than in the controls, no other difference in blood indicators was found. D-003 did not increase the frequency of neoplastic and non-neoplastic lesions compared with the controls. The occurrence of all malignant and mammary tumours in D-003-treated females was lower than in the controls. The lesions observed were consistent with spontaneous lesions reported in this species. In conclusion, D-003 is not toxic or carcinogenic when given orally to Sprague Dawley rats up to 1500 mg/kg for 2 years, and 1500 mg/kg was a not-observable effect dose.

D-004, a lipid extract of royal palm (Roystonea regia) fruits that contains a reproducible mixture of fatty acids, has been shown to prevent testosterone and phenylephrine-induced prostate hyperplasia in rodents. This study investigated the long-term oral toxicity of D-004 in rats. Rats from both sexes were randomized into four groups (20 rats sex/group): a control and three treated with D-004 (800, 1500 or 2000 mg/kg/day, respectively). At study completion, rats were sacrificed under anaesthesia. Determinations of blood biochemical and haematological parameters and organ weight were done. Also, necropsy and histopathological studies were performed. Four of 160 rats died before study completion. No clinical signs of toxicity were observed throughout the study. Food and water consumption, bodyweight, blood biochemical and haematological parameters, organ weight ratios and histopathological findings were similar in control and treated groups. The histological lesions found in treated animals are commonly present in this specie and strain according to literature and our historical data. In conclusion, long-term (12 months) oral treatment of rats with D-004 (800-2000 mg/kg/day) did not show evidences of D-004-related toxicity under our conditions. The highest dose tested (2000 mg/kg) was a no-observed adverse effect level in this study.

EPO-018B, a synthetic peptide-based erythropoiesis stimulating agent (ESA), is coupled to polyethylene glycol (PEG) and designed to specifically bind and activate the erythropoietin (EPO) receptor to result in production of red blood cells. This study was designed to evaluate the potential subchronic toxicity of EPO-018B for cynomolgus monkeys and Sprague-Dawley rats both at 0,0.5, 5 and 50mg/kg every week for five weeks, followed by 6-week recovery for rats and 12-week recovery for monkeys. The No Observed Adverse Effect Level (NOAEL) for rats and monkeys were both considered to be at least 0.5mg/kg/day, the minimum toxic dose to be 5.0mg/kg/day and the severe toxic dose to be more than 50.0mg/kg/day. The toxicological effects included the exaggerated pharmacology and secondary sequelae that resulted from an erythropoiesis-stimulating agent treatment to healthy animals. Most treatment induced effects were reversible or showed ongoing recovery upon discontinuation of treatment. The anticipated patient population for EPO-018B treatment is targeted to be the anemia patients caused by chronic renal failure or chemotherapy against to cancer and is expected to have an ideal clinical application prospect.

The murine local lymph node assay is a predictive test for the identification of contact allergens. This paper provides a historical background to the development of the assay and describes the performance of a recently completed interlaboratory trial designed to evaluate further the utility of the method as an alternative or adjunct to guinea-pig predictive tests. On the basis of these and supplementary investigations, a number of recommendations can be made regarding the use and interpretation of the local lymph node assay. Finally, a number of issues arising from recent studies are discussed, including comparisons of the local lymph node assay with guinea-pig methods.

The objective of this study is to evaluate the relationship between dietary AA and hemoglobin adducts using the National Health and Nutrition Examination Survey (NHANES, 2003-04). Measured acrylamide (AA-Hb) and glycidamide (Gly-Hb) hemoglobin adducts for over 7000 participants >3 years, 24-h dietary recall, food frequency questionnaire (FFQ), lifestyle and demographic data, and anthropometric measurements are available from NHANES (2003-04). The 24-h dietary recall and FFQ data were combined with AA concentration data in food from the US FDA to estimate "usual" AA dietary exposure. The associations between dietary AA and AA-Hb and Gly-Hb were evaluated using linear regression models with smoking, age, gender, energy and macronutrient intake, body surface area, and activity level as covariates. Dietary AA positively correlates with AA-Hb and Gly-Hb (p<0.05) but the correlation is small (R-Squared<3.5%). Relative to the background adduct levels, the incremental increase in AA-Hb and Gly-Hb from average dietary AA is small (7% and 9% for AA-Hb and Gly-Hb, respectively). Non-dietary sources of exposure, measurement errors associated with the use of the FFQ, and uncertainty in the data on AA levels in foods are possible explanations for the observed lack of association between dietary AA and AA-Hb and Gly-Hb.

Organotellurium(IV) compounds have been reported to have multiple biological activities including cysteine protease-inhibitory activity, mainly cathepsin B. As cathepsin B is a highly predictive indicator for prognosis and diagnosis of cancer, a possible antitumor potential for these new compounds is expected. In this work, it was investigated the effectiveness of organotellurium(IV) RT-04 to produce lethal effects in the human promyelocytic leukaemia cell line HL60. Using the MTT tetrazolium reduction test, and trypan blue exclusion assay, the IC50 for the compound after 24 h incubation was 6.8 and 0.35 microM, respectively. Moreover, the compound was found to trigger apoptosis in HL60 cells, inducing DNA fragmentation and caspase-3, -6, and -9 activations. The apoptsosis-induced by RT-04 is probably related to the diminished Bcl-2 expression, observed by RT-PCR, in HL60-treated cells. In vivo studies demonstrated that the RT-04 treatment (2.76 mg/kg given for three consecutive days) produces no significant toxic effects for bone marrow and spleen CFU-GM. However, higher doses (5.0 and 10 mg/kg) produced a dose-dependent reduction in the number of CFU-GM of RT-04-treated mice. These results suggest that RT-04 is able to induce apoptosis in HL60 cells by Bcl-2 expression down-modulation. Further studies are necessary to better clarify the effects of this compound on bone marrow normal cells.

Monensin, a well known ionophore antibiotic, may cause severe damage in neuronal cells by altering Na+/K+-ATPase and Ca2+-ATPase. We investigated whether IRFI-042, a synthetic analogue of vitamin E, may block lipid peroxidation in neuronal cells and protect against monensin neurotoxicity in chicks. Monensin toxicity was induced in chicks by once-daily administration (150 mg/kg by oral gavages), for 8 days. Sham animals received a saline solution and were used as controls. All animals were randomized to receive either IRFI-042 (20 mg/kg) or its vehicle. Survival rate, brain lipid peroxidation, mRNA for neuronal and inducible nitric oxide synthases (nNOS and iNOS) and brain histological evaluations, including immunohistochemical expression of nNOS and iNOS were performed. Monensin administration decreased survival rate, induced behavioural changes, increased brain lipid peroxidation, reduced brain nNOS mRNA and immunostaining and enhanced iNOS mRNA and immunostaining in the brain in chicks. IRFI-042 significantly improved the survival rate and counteracted monensin-induced changes in chick brains. Our data suggest that monensin is responsible of neurotoxicity in chicks by inducing oxidative stress/lipid peroxidation and that IRFI-042 might represent a useful pharmacological approach to protect against the neuronal damage induced by this monovalent carboxylic ionophorous polyether antibiotic.

Acrylamide (CH(2)CHCONH(2), CAS Registry No. 79-06-1) is an industrial chemical used since the 1950s as a chemical intermediate in the production of polyacrylamides, which are used as flocculants for clarifying drinking-water and other industrial applications. The neurotoxicity of acrylamide in humans is well known from occupational and accidental exposures. In addition, experimental studies with acrylamide in animals have shown reproductive, genotoxic and carcinogenic properties. Acrylamide may be formed when foods, particularly those that are high in carbohydrates and low in protein, are subjected to high temperatures during cooking or other thermal processing.

Sudan I is generally considered mutagenic based on various in vitro and in vivo tests and is carcinogenic in the rat. Dose-response modelling of the data for hepatocellular adenomas in male rats gave a BMDL(10) of 7.3mg/kg-bw/day. Sudan I is an unauthorised substance that might be present in food intermittently. The great variability and uncertainties in the human exposure data which are country specific, depending on consumption patterns and methodology used, resulted in a large range of MOE values (from 30 to 2,000,000).

HCFC-141b is one of the chemicals being considered as a replacement for CFC 11 in solvent and foam-blowing applications. Teratology studies were conducted in both rats and rabbits and a two-generation reproduction inhalation toxicity study was conducted in rats. The pregnant rabbits were exposed to levels of 0 (control), 1400, 4200 and 12,600 ppm HCFC-141b from day 7 to day 19 of gestation (6 hr/day). There was no evidence of developmental or teratogenic effects on the foetuses. The pregnant rats in the teratology study were exposed to levels of 0 (control), 3200, 8000 and 20,000 ppm from days 6 to 15 of gestation (6 hr/day). In the 20,000 ppm exposure group, there was an increase in implantation losses; furthermore, in this group, foetal weights tended to be lower than controls. As with the rabbits, there was no evidence of a teratogenic effect. The reproduction study was conducted at exposure levels of 0, 2000, 8000 and 20,000 ppm, 7 days/wk starting approximately 10 wk before the first pairing. Adult rats exposed at 20,000 ppm (and, to a lesser extent, those exposed to 8000 ppm) showed increases in water intake, slight increases in food consumption, and decreases in body weight. Following the mating of the F0 parents, there were fewer litters in the 20,000 ppm exposure level group than in controls. When these parents were then paired with different partners, again, the number of litters was lower in the 20,000 ppm group, although most of the animals that did not produce litters the first time mated successfully the second time. When the F1 animals were mated to produce the second generation, the number of litters was comparable for all groups. In the second F0 mating and the F1 mating, the number of pups per litter was lower at 20,000 ppm; although birth weights were comparable, body weight gain tended to be slower in the high-level exposure group. Survival was good in all groups. At 8000 ppm no significant effects were observed in the pups and only minimal signs in the adults. The 2000 ppm exposure level represented a clear no-observed-effect level for all indices.

A toxicologic and dermatologic review of 1,1-dimethyl-2-phenylethyl butyrate when used as a fragrance ingredient is presented. 1,1-Dimethyl-2-phenylethyl butyrate is a member of the fragrance structural group aryl alkyl alcohol simple acid esters (AAASAE). The AAASAE fragrance ingredients are prepared by reacting an aryl alkyl alcohol with a simple carboxylic acid (a chain of 1-4 carbons) to generate formate, acetate, propionate, butyrate, isobutyrate and carbonate esters. This review contains a detailed summary of all available toxicology and dermatology papers that are related to this individual fragrance ingredient and is not intended as a stand-alone document. Available data for 1,1-dimethyl-2-phenylethyl butyrate were evaluated, then summarized, and includes: physical properties, acute toxicity, skin irritation, mucous membrane (eye) irritation, skin sensitization, and genotoxicity data. A safety assessment of the entire AAASAE will be published simultaneously with this document. Please refer to Belsito et al. (2012) for an overall assessment of the safe use of this material and all AAASAE in fragrances. Belsito, D., Bickers, D., Bruze, M., Calow, P., Dagli, M., Fryer, A.D., Greim, H., Hanifin, J.H., Miyachi, Y., Saurat, J.H., Sipes, I.G., 2012. A toxicologic and dermatologic assessment of aryl alkyl alcohol simple acid esters when used as fragrance ingredients.

A toxicologic and dermatologic review of 1,1-dimethyl-2-phenylethyl acetate when used as a fragrance ingredient is presented. 1,1-Dimethyl-2-phenylethyl acetate is a member of the fragrance structural group Aryl Alkyl Alcohol Simple Acid Esters (AAASAE). The AAASAE fragrance ingredients are prepared by reacting an Aryl Alkyl Alcohol with a simple carboxylic acid (a chain of 1-4 carbons) to generate formate, acetate, propionate, butyrate, isobutyrate and carbonate esters. This review contains a detailed summary of all available toxicology and dermatology papers that are related to 1,1-dimethyl-2-phenylethyl acetate and is not intended as a stand-alone document. Available data were evaluated, then summarized, and includes: physical properties; acute toxicity; skin irritation; mucous membrane (eye) irritation; skin sensitization; elicitation; and toxicokinetics data. A safety assessment of the entire AAASAE will be published simultaneously with this document. Please refer to Belsito et al. (2012) for an overall assessment of the safe use of this material and all AAASAE in fragrances. Belsito, D., Bickers, D., Bruze, M., Calow, P., Dagli, M., Fryer, A.D., Greim, H., Hanifin, J.H., Miyachi, Y., Saurat, J.H., Sipes, I.G., 2012. A toxicologic and dermatologic assessment of Aryl Alkyl Alcohol simple acid esters when used as fragrance ingredients.

A toxicologic and dermatologic review of 1,1-dimethyl-2-phenylethyl formate when used as a fragrance ingredient is presented. 1,1-Dimethyl-2-phenylethyl formate is a member of the fragrance structural group Aryl Alkyl Alcohol Simple Acid Esters (AAASAE). The AAASAE fragrance ingredients are prepared by reacting an aryl alkyl alcohol with a simple carboxylic acid (a chain of 1-4 carbons) to generate formate, acetate, propionate, butyrate, isobutyrate and carbonate esters. This review contains a detailed summary of all available toxicology and dermatology papers that are related to this individual fragrance ingredient and is not intended as a stand-alone document. Available data for 1,1-dimethyl-2-phenylethyl formate were evaluated, then summarized, and includes: physical properties; acute toxicity; skin irritation; mucous membrane (eye) irritation; skin sensitization; and genotoxicity data. A safety assessment of the entire AAASAE will be published simultaneously with this document. Please refer to Belsito et al., 2012 for an overall assessment of the safe use of this material and all AAASAE in fragrances. Belsito, D., Bickers, D., Bruze, M., Calow, P., Dagli, M., Fryer, A.D., Greim, H., Hanifin, J.H., Miyachi, Y., Saurat, J.H., Sipes, I.G., 2012. A toxicologic and dermatologic assessment of aryl alkyl alcohol simple acid esters when used as fragrance ingredients.

The acute and subchronic toxicity of 1,1-dichloro-1-fluoroethane (HCFC-141b), a CFC alternative, was evaluated in several acute and subchronic studies to assist in establishing proper handling guides. Data from acute toxicity studies in rats and rabbits demonstrated that HCFC-141b has very low acute toxicity. HCFC-141b was not a skin irritant, but was a mild eye irritant, in rabbits and was not a skin sensitizer in guinea pigs. Skin application of HCFC-141b to rabbits at 2000 mg/kg body weight produced no adverse effects. Oral administration at 5000 mg/kg body weight did not cause any deaths or clinical signs of toxicity in rats. The 4-hr LC50 for HCFC-141b was about 62,000 ppm in rats. Repeated exposures of rats for 6 hr/day, 5 days/wk for up to 90 days at concentrations of 2000, 8000 or 20,000 ppm did not result in significant adverse effects. Minor, but dose-dependent, reductions in body weight were observed in male and female rats during the 90-day study. Decreased responsiveness was also observed in rats but only at 20,000 ppm. An increase in serum cholesterol or triglycerides was observed in male and female rats at 20,000 ppm, and in males at 8000 ppm. No specific organ pathology was noted in these subchronic inhalation studies. The no-observable-adverse-effect level (NOAEL) from these studies was 8000 ppm. Results from other studies demonstrate that HCFC-141b was not neurotoxic in rats. As with trichlorofluoroethane (CFC-11), a cardiac sensitization response to an intravenous epinephrine challenge occurred in dogs with HCFC-141b at 5000 ppm and higher concentrations in experimental screening studies.

1,1-Bis(tert-butylperoxy)-3.3.5-trimethylcyclohexane (BBTC) is widely used in the manufacture of rubber. The present carcinogenicity study in B6C3F1 mice was carried out in order to assess its potential to induce tumours. BBTC was administered at dietary levels of 0 (control), 0.25 and 0.5% for 78 wk; these dose levels were selected on the basis of a subchronic toxicity study, in which body weights were depressed to less than 90% of the control group values and swelling of hepatocytes was histologically evident in animals fed 1% BBTC or more in the diet. Neoplasms were found in all groups, including the control group, but there were no significant differences between groups of either sex in mortality, tumour incidences or tumour distribution. All tumours were considered to be spontaneous because of the similarity to background data for B6C3F1 mice. This study thus provides no evidence of carcinogenicity of BBTC in B6C3F1 mice.

A toxicologic and dermatologic review of 1,1-dimethyl-2-phenylethyl isobutyrate when used as a fragrance ingredient is presented. 1,1-Dimethyl-2-phenylethyl isobutyrate is a member of the fragrance structural group Aryl Alkyl Alcohol Simple Acid Esters (AAASAE). The AAASAE fragrance ingredients are prepared by reacting an aryl alkyl alcohol with a simple carboxylic acid (a chain of 1-4 carbons) to generate formate, acetate, propionate, butyrate, isobutyrate and carbonate esters. This review contains a detailed summary of all available toxicology and dermatology papers that are related to this individual fragrance ingredient and is not intended as a stand-alone document. Available data for 1,1-dimethyl-2-phenylethyl isobutyrate were evaluated, then summarized, and includes physical properties data. A safety assessment of the entire AAASAE will be published simultaneously with this document. Please refer to Belsito et al., 2012 for an overall assessment of the safe use of this material and all AAASAE in fragrances. Belsito, D., Bickers, D., Bruze, M., Calow, P., Dagli, M., Fryer, A.D., Greim, H., Hanifin, J.H., Miyachi, Y., Saurat, J.H., Sipes, I.G., 2012. A toxicological and dermatological assessment of aryl alkyl alcohol simple acid esters derivatives when used as fragrance ingredients.

A toxicologic and dermatologic review of 1,1-dimethyl-2-phenylethyl propionate when used as a fragrance ingredient is presented. 1,1-Dimethyl-2-phenylethyl propionate is a member of the fragrance structural group Aryl Alkyl Alcohol Simple Acid Esters (AAASAE). The AAASAE fragrance ingredients are prepared by reacting an aryl alkyl alcohol with a simple carboxylic acid (a chain of 1-4 carbons) to generate formate, acetate, propionate, butyrate, isobutyrate and carbonate esters. This review contains a detailed summary of all available toxicology and dermatology papers that are related to this individual fragrance ingredient and is not intended as a stand-alone document. Available data for 1,1-dimethyl-2-phenylethyl propionate were evaluated, then summarized, and includes: physical properties; acute toxicity; skin irritation; and skin sensitization data. A safety assessment of the entire AAASAE will be published simultaneously with this document. Please refer to Belsito et al. (submitted for publication) for an overall assessment of the safe use of this material and all AAASAE in fragrances. Belsito, D., Bickers, D., Bruze, M., Calow, P., Dagli, M., Fryer, A.D., Greim, H., Hanifin, J.H., Miyachi, Y., Saurat, J.H., Sipes, I.G., submitted for publication. A toxicologic and dermatologic assessment of aryl alkyl alcohol simple acid esters when used as fragrance ingredients.

The effects of DDT on the energy-related functions of rat-liver mitochondria were examined. ADP-stimulated respiration was much more sensitive to inhibition by DDT than was uncoupler-stimulated respiration when succinate or ascorbate/TMPD was used as the substrate. Ca2+ uptake driven by ATP hydrolysis was inhibited by DDT. These results indicate that DDT inhibits ATPase itself. In addition, DDT blocked succinate dehydrogenase and the cytochrome b-c span of the electron transport chain, which also secondarily reduced ATP synthesis. The uncoupling action due to DDT was only seen at high concentrations with ascorbate/TMPD as the substrate. However, this action was masked because of the increased inhibition of the electron transport chain when the substrate was changed to succinate.

Three chromogenic products of AHTN have been detected after photo-oxidation and shown to react with glycine or albumin, giving rise first to a blue color, followed by pink and, finally, a dark green colour. The absorption spectrum associated with the late green colour showed an increased absorbance in the long wavelength region of the spectrum, similar to the green colour extracted from the liver of AHTN-treated animals. The colour produced by the chromogenic derivatives of AHTN and by o-diacetylbenzene (a model chromogenic compound) were tightly bound to the protein pellet and resistant to acidic pH, unlike the colour from the ninhydrin reaction. The dark green colour produced in the liver by feeding AHTN to rats was also tightly bound to proteins and stable to acidic pH. These results suggest that both the photo-oxidized chromogenic derivatives of AHTN and o-diacetylbenzene, produce coloured derivatives with amino acids and proteins by a mechanism unrelated to ninhydrin. They also suggest that a chromogenic derivative of AHTN, produced in vivo during prolonged treatment with high doses of AHTN, may be responsible for the green colour of the livers and other tissues from treated animals. The data suggest that the AHTN-derived chromogenic material is metabolite-related rather than representative of a toxic process, although further work is necessary to confirm this hypothesis.

The teratogenic potential of 1,1,3,3-tetrabutylurea (TBU) was evaluated in the Crl:CD(SD)BR rat. Doses of 25, 50 or 100 mg TBU/rat/day in 0.5 ml dimethyl phthalate were applied to the shaven dorsal skin on days 6-15 of gestation, the day on which a sperm-positive vaginal smear was present being designated day 1. The rats were killed 1 day before natural delivery and the foetuses were examined for external development, structure and integrity of internal tissues and organs, and skeletal development. No maternal effects were seen in rats exposed to 25 mg TBU, but skin irritation and a reduction in maternal body-weight gains were seen in rats treated with either 50 or 100 mg/day, the effects being more pronounced in the 100-mg/day group. In the latter group, the number of pregnancies maintained was reduced and the number of resorptions per litter, calculated only on the litters with resorptions, was increased. Foetuses derived from the females treated with 100 mg/day were slightly smaller than the controls but were structurally normal. The outcome of pregnancy was unaltered in rats given either 25 or 50 mg TBU/day. No increase in malformed foetuses was observed in any of the test groups. Under the conditions of this study, TBU was not teratogenic when applied dermally to rats at doses up to 100 mg/day.

7-Acetyl-1,1,3,4,4,6-hexamethyl-1,2,3,4-tetrahydronaphthalene (AHTN) is used as a fragrance material in a wide variety of consumer products. Because of its widespread exposure, a 90-day oral feeding study, with 4-week recovery periods for selected rats, was conducted. AHTN was added to the diet of rats at levels calculated to result in mean daily doses of 1.5, 5, 15 or 50 mg AHTN/kg body weight/day. On completion of the treatment period, 3 males and 3 females from each of the high dose groups and controls were maintained for a treatment free period of 4 weeks. There were no adverse effects revealed upon clinical examination or following extensive histopathological examinations. Histopathological examination of the prostate, seminal vesicles, mammary gland and testes of males and ovaries, mammary gland, uterus and vagina of females, undertaken on all animals in all test groups, revealed no evidence of hormonal effects of AHTN. A statistically significant decrease in body weight gain was observed in both sexes in the high dose group only. Statistically significant effects were observed in hematology and blood chemistry, although these effects were all within the range for historical controls and were not proportional to dose. A green to dark brown coloration in the livers and mesenteric lymph nodes was also seen in high dose animals. At the end of the treatment-free period, the color change was almost completely reversed; one high dose male still had green colored lymph nodes, but the liver appeared normal. A green coloration of the lacrimal glands in females, but not males, was also seen in 8/12, 4/15 and in 1 female given 50, 15 and 5 mg/kg body weight/day, respectively. This green color was still present in 2/3 of the high dose females after the treatment-free period. Microscopic examination of unstained sections of frozen livers under UV illumination did not reveal any fluorescence that might have been consistent with porphyrin accumulation. These findings were clearly related to administration of AHTN, but were not accompanied by any histopathological changes. In discolored livers, all fractions of liver homogenate were abnormally colored; the change was most prominent in the mitochondria. Some dissolved pigment was obtained by extraction of liver homogenates with DMSO/trichloroacetic acid mixtures, but its identity remains to be established. Further work on the mechanism of production of the abnormal color is in progress. Based on these results, the 90-day conservative no-observed-effect level (NOAEL) is 1.5 mg/kg body weight/day.

A toxicologic and dermatologic review of octahydro-7,7,8,8-tetramethyl-2,3b-methano-3bH-cyclopenta[1,3]cyclopropa[1,2]benzene-4-methanol when used as a fragrance ingredient is presented.

A toxicologic and dermatologic review of 1,2-ethanediol, 1-phenyl-, 1,2-diacetate when used as a fragrance ingredient is presented. 1,2-Ethanediol, 1-phenyl-, 1,2-diacetate is a member of the fragrance structural group Aryl Alkyl Alcohol Simple Acid Esters (AAASAE). The AAASAE fragrance ingredients are prepared by reacting an aryl alkyl alcohol with a simple carboxylic acid (a chain of 1-4 carbons) to generate formate, acetate, propionate, butyrate, isobutyrate and carbonate esters. This review contains a detailed summary of all available toxicology and dermatology papers that are related to this individual fragrance ingredient and is not intended as a stand-alone document. Available data for 1,2-ethanediol, 1-phenyl-, 1,2-diacetate were evaluated, then summarized, and includes physical properties data. A safety assessment of the entire AAASAE will be published simultaneously with this document. Please refer to Belsito et al. (2012) for an overall assessment of the safe use of this material and all AAASAE fragrances. Belsito, D., Bickers, D., Bruze, M., Calow, P., Dagli, M., Fryer, A.D., Greim, H., Hanifin, J.H., Miyachi, Y., Saurat, J.H., Sipes, I.G., 2012. A toxicological and dermatological assessment of aryl alkyl alcohol simple acid ester derivatives when used as fragrance ingredients.

The effect of the plant cellulose metamucil on the tumorigenicity of 1,2-dimethylhydrazine dihydrochloride (1,2-DMH) was studied in random-bred Swiss mice. Three groups of mice, which were 5, 6 and 6 weeks old at the beginning of the experiment, were given the following treatments: (1) metamucil (20%, w/w) in powdered diet for their lifespan; (2) 1,2-DMH, ten weekly subcutaneous injections at 20 mg/kg body weight; (3) combination of treatments given to groups 1 and 2. The administration of metamucil enhanced the appearance of colon tumours induced by 1,2-DMH in males only. Metamucil had no statistically significant effect on the development of tumours elicited by 1,2-DMH at seven additional sites. It was expected that a high amount of dietary fibre would inhibit carcinogenesis in the large intestine. Instead, metamucil increased the incidence of colon tumours induced by 1,2-DMH, although only in males.

Sprague-Dawley rats were administered 1,2-diethylbenzene (1,2-DEB) by gavage on gestational days (GD) 6 through 20 at dose levels of 0 (corn oil), 5, 15, 25 or 35 mg/kg. The dams were euthanized on GD21 and the offspring were weighed and examined for external, visceral and skeletal alterations. Maternal toxicity, indicated by significant decreases in body weight gain and food consumption, was observed at doses of 15 mg/kg and above. Developmental toxicity, expressed as significantly reduced foetal body weights, was seen at doses of 15 mg/kg and higher. There was no evidence of embryolethal or teratogenic effects at any dose tested. The placental transfer of 1,2-DEB was examined after a single oral dose of 25 mg [14C]1,2-DEB/kg on GD18. Maternal and foetal tissues were collected at intervals from 1 to 48 hours. Placental and foetal tissues accounted for less than 0.35% of the administered dose. Levels of radiocarbon in foetuses were lower than those in maternal plasma and placenta at all time points. Analysis performed at 1, 2 and 4 hours indicated that ethyl acetate extractable (acidic) metabolites were predominant in the maternal plasma while n-hexane extractable (neutral) compounds represented the major part of radioactivity in the placenta and foetus. In conclusion, this study demonstrated that 1,2-DEB causes mild foetotoxicity at maternal toxic doses and that the exposure of the developing rat foetus to 1,2-DEB and/or metabolites after maternal administration of 1,2-DEB in late gestation is small.

3-Monochloropropane-1,2-diol (alpha-chlorohydrin, 3-MCPD) is a well-known contaminant, which has been detected in a wide range of foods and ingredients, and is also a suspected cause of cancer. In this study, the carcinogenicity of 3-MCPD in SD rats was investigated. Groups of 50 male and 50 female rats were exposed for two years to drinking water containing 0, 25, 100 or 400ppm 3-MCPD. The body weights and water consumptions of the male and female rats given 400ppm 3-MCPD were significantly lower than those of the controls. The incidences of renal tubule adenomas or carcinomas and Leydig cell tumors occurred with dose-related positive trends in male rats. The incidences of renal tubule carcinomas and Leydig cell tumors were significantly increased in male rats given 400ppm 3-MCPD. The incidence of renal tubule adenomas showed a positive trend in female rats, which was significant in 400ppm 3-MCPD group. In conclusion, there was clear evidence of the carcinogenic activity of 3-MCPD in male SD rats, based on the increased incidences of renal tubule carcinomas and Leydig cell tumors. There was some evidence of the carcinogenic activity of 3-MCPD in female SD rats, based on the increased incidence of renal tubule adenomas.

5-Azacytidine is being used for reactivation of tumor suppressor genes. However, its administration during DNA repair pontentiates hepatocarcinogenesis. We observed chemopreventive activities by vitamin A and beta-carotene during early hepatocarcinogenesis. Thus, in the present study we evaluated vitamin A and beta-carotene chemopreventive potential during early hepatocarcinogenesis potentiated by 5-azacytidine. Wistar rats received vitamin A (VAA group), beta-carotene (betaCA group) or corn oil (CO and COA groups). After three weeks of treatment, all animals were initiated with 1,2-dimethylhydrazine. Twelve hours later VAA, betaCA and COA groups received a single dose of 5-Azc. Hepatocytes were selected/promoted by 2-acetylaminofluorene and 70% partial hepatectomy. All animals were sacrificed six weeks after initiation. Compared to CO group (without 5-azacytidine), COA group presented higher (p<0.05) nodule multiplicity, larger (p<0.05) gamma-GT positive lesions that occupied a larger (p<0.05) area of liver section. Compared to COA group, VAA group presented decreased (p<0.05) nodule multiplicity while betaCA group tended to present smaller gamma-GT positive lesions and to decrease occupied liver section. These results reinforce vitamin A and beta-carotene chemopreventive potential. Considering that 5-azacytidine potentiates hepatocarcinogenesis, more studies are needed to elucidate the efficacy and safety of this drug for cancer control.

Ginger (Zingiber officinale Roscoe) has been proposed as a promising candidate for cancer prevention. Its modifying potential on the process of colon carcinogenesis induced by 1,2-dimethylhydrazine (DMH) was investigated in male Wistar rats using the aberrant crypt foci (ACF) assay. Five groups were studied: Groups 1-3 were given four s.c. injections of DMH (40 mg/kg b.w.) twice a week, during two weeks, whereas Groups 4 and 5 received similar injections of EDTA solution (DMH vehicle). After DMH-initiation, the animals were fed a ginger extract mixed in the basal diet at 0.5% (Group 2) and 1.0% (Groups 3 and 4) for 10 weeks. All rats were killed after 12 weeks and the colons were analyzed for ACF formation and crypt multiplicity. The rates of cell proliferation and apoptosis were also evaluated in epithelial colonic crypt cells. Dietary consumption of ginger at both dose levels did not induce any toxicity in the rats, but ginger meal at 1% decreased significantly serum cholesterol levels (p<0.038). Treatment with ginger did not suppress ACF formation or the number of crypts per ACF in the DMH-treated group. Dietary ginger did not significantly change the proliferative or apoptosis indexes of the colonic crypt cells induced by DMH. Thus, the present results did not confirm a chemopreventive activity of ginger on colon carcinogenesis as analyzed by the ACF bioassay and by the growth kinetics of the colonic mucosa.

Our current study is an effort to identify a potent chemopreventive agent against colon cancer. Here we have investigated the efficacy of hesperetin on tissue lipid peroxidation, antioxidant defense system and colonic histoarchitecture in male Wistar rats in colon carcinogenesis. Rats in groups 3, 4, 5 and 6 were treated with DMH (20 mg kg body weight s.c.) once a week for 15 weeks. Group 1 rats received modified pellet diet and served as control; group 2 received modified pellet diet along with hesperetin (20mg/kg body weight, p.o., every day); and hesperetin was given to the rats as in-group 2 during the initiation, post-initiation and entire period stages of colon carcinogenesis. Lipid peroxidation was studied by measuring the formation of thiobarbituric acid reactive substances (TBARS), lipid hydroperoxides (LOOH) and conjugated dienes (CD), and superoxide dismutase (SOD), catalase (CAT), glutathione peroxidase (GPX), glutathione reductase (GR), reduced glutathione (GSH), in the liver and colonic tissues of DMH administered rats. (1) Decreased levels of lipid peroxidation in the colonic tissues; (2) decreased activities of antioxidant enzymes SOD, CAT, GPX, GR and GSH levels in the tissues on DMH treatment. Hesperetin supplementation during the initiation, post-initiation and entire period stages of carcinogenesis significantly reversed these activities. These results indicate that hesperetin may be a potential chemopreventive agent against DMH-induced colon cancer.

alpha-Eleostearic acid is one of the conjugated linolenic acids from tung oil, which is obtained from the seeds of Aleurites fordii. The effects of dietary alpha-eleostearic acid (18:3, n-5) on the post-initiation period of 7,12-dimethylbenz[a]anthracene (DMBA) and 1,2-dimethylhydrazine (DMH)-induced mammary and colon carcinogenesis were examined using female Sprague-Dawley (SD) rats. For initiation, rats were given subcutaneous injections of 40mg/kg body weight (5 times) and 20mg/kg body weight (3 times) of DMH during the age of 6-8 weeks and a single intragastric administration of 50mg/kg body weight of DMBA at 9 weeks. Then, the animals were treated with 0%, 0.01%, 0.1% or 1.0% alpha-eleostearic acid for 34 weeks. Control rats received the basal diet alone or 1.0% alpha-eleostearic acid without prior initiation treatment. All surviving animals were killed at week 37 of the experiment. There were no statistically significant alterations in any of the parameters for either mammary or colon tumors. These results thus indicate that alpha-eleostearic acid does not exert clear modification effects on DMBA and DMH-induced mammary and colon carcinogenesis, at least under the present experimental conditions.

Colon cancer risk may be influenced by phase I and II xenobiotic-metabolizing enzyme systems. The chemopreventive agent gallic acid (GA), a plant polyphenol, is found in various natural products. Our aim was to evaluate the potential role of GA on drug-metabolizing enzymes in 1,2-dimethyl hydrazine (DMH) induced rat colon carcinogenesis. The total experimental duration was 30 weeks. The effect of GA (50 mg/kg b.w.) on the activities of phase I enzymes (cytochrome P450 and cytochrome b5) and phase II enzymes (glutathione S-transferase, DT-diaphorase and gamma glutamyl transpeptidase) were assessed in the liver and colonic mucosa and the colons were also examined visually. In DMH induced rats, there was a decrease in the activities of phase II enzymes and an increase in the activities of phase I enzymes. On GA supplementation, there was a significant increase in the activities of phase II enzymes and a significant decrease in the activities of phase I enzymes, in addition to the decreased tumor incidence. Histopathological changes also confirm this. Thus, the marked potential of GA in modulating the phase I and II xenobiotic-metabolizing enzymes suggests that GA may have a major impact on colon cancer chemoprevention.

A toxicologic and dermatologic review of 4-(1,2-epoxy-2,6,6-trimethylcyclohexyl)-3-buten-2-one when used as a fragrance ingredient is presented.

N-Nitroso-N-(3-keto-1,2-butanediol)-3'-nitrotyramine (NO-NTA) is a product of model browning system generated in the presence of sodium nitrite. The chemical structure of this compound has been confirmed by UV, mass and nuclear magnetic resonance, and infrared spectroscopy in our previous study. A two-stage transformation protocol was used to chemically transform the mouse embryo fibroblasts C3H10T1/2 cells. To initiate transformation, the cells were treated with benzo[a]pyrene (BaP) (0.1 mg/ml), and NO-NTA (0.01, 0.1 and 1 mg/ml) was employed subsequently to complete the transformation process. Malignant transformed foci were formed in BaP-initiated and NO-NTA promoted C3H10T1/2 cells after 8 wk. Cells treated with NO-NTA alone failed to induce transformation. However, cells initiated with BaP and promoted by cells initiated with BaP and promoted by NO-NTA demonstrated oncogenic properties. Cell lines transformed with NO-NTA-transformed colonies exhibited enhanced growth rate, anchorage independence and tumorigenicity in animals relative to parent cells. These results indicate that NO-NTA is a new tumour promoter and may induce tumour promotion by two-stage oncogenesis. Further studies on the mechanism of action of NO-NTA are now in progress.

Bowman-Birk inhibitors (BBIs) are protein molecules containing two inhibitory domains for enzymes similar to trypsin and chymotrypsin. Interest in these inhibitors arose from their properties against the cancer chemically induced by 1,2-dimethylhydrazine (DMH). In this study the effect of two BBI preparations (from Glycine max and Macrotyloma axillare) were evaluated for the prevention of colorectal neoplasia induced by intraperitoneal injections of DMH, given at a dose of 30 mg/kg, during 12 weeks. Mice treated with DMH presented histopathological alterations consistent with tumor development, augmented CD44 expression and increased proteasome peptidase activities. Lysosomal fractions, obtained from the intestines, were chromatographed in a Sepharose-BBI column and increased activity for trypsin and chymotrypsin-like proteases recovered from DMH-treated animals. In parallel, mice treated for eight weeks with BBIs showed a decrease in the chymotrypsin and trypsin-like proteasome activities compared to animals fed on normal diet. For the groups receiving simultaneous treatment with DMH and BBIs, dysplasic lesions were not observed and proteasome peptidase activities were similar to the control group after the 24th week. These results suggest that the mechanism by which BBIs could prevent the appearance of pre neoplastic lesions is associated with inhibition of both the lysosomal and proteasome-dependent proteolytic pathways.

1,2-Benzisothiazolin-3-one (BIT; CAS # 2634-33-5) is a preservative used in consumer products. Dermal exposure to BIT at sufficient dose and duration can produce skin sensitization and allergic contact dermatitis in animals and susceptible humans.The purpose of this study is to derive a maximal concentration of BIT in various consumer products that would result in exposures below the No Expected Sensitization Induction Level (NESIL), a dose below which skin sensitization should not occur. A screening level exposure estimate was performed for several product use scenarios with sunscreen, laundry detergent, dish soap, and spray cleaner. We calculated that BIT concentrations below the following concentrations of 0.0075%, 0.035%, 0.035%, 0.021% in sunscreen, laundry detergent, dish soap, and spray cleaner, respectively, are unlikely to induce skin sensitization. We completed a pilot study consisting of bulk sample analysis of one representative product from each category labelled as containing BIT, and found BIT concentrations of 0.0009% and 0.0027% for sunscreen and dish soap, respectively. BIT was not detected in the laundry detergent and spray cleaner products above the limit of detection of 0.0006%. Based on publically available data for product formulations and our results, we were able to establish that cleaning products and sunscreens likely contain BIT at concentrations similar to or less than our calculated maximal safe concentrations and that exposures are unlikely to induce skin sensitization in most users.

3-monochloropropane-1,2-diol (3-MCPD) is a member of a group of chemicals known as chloropropanols. It is found in many foods and food ingredients as a result of food processing. 3-MCPD is regarded as a rat carcinogen known to induce Leydig-cell and mammary gland tumours in males and kidney tumours in both genders. The aim of our study was to clarify the possible involvement of genotoxic mechanisms in 3-MCPD induced carcinogenicity at the target organ level. For that purpose, we evaluated DNA damages in selected target (kidneys and testes) and non-target (blood leukocytes, liver and bone marrow) male rat organs by the in vivo alkaline single cell gel electrophoresis (comet) assay, 3 and 24 h after 3-MCPD oral administration to Sprague-Dawley and Fisher 344 adult rats. 3-MCPD may be metabolised to a genotoxic intermediate, glycidol, whereas the predominant urinary metabolite in rats following 3-MCPD administration is beta-chlorolactic acid. Therefore, we also studied the DNA damaging effects of 3-MCPD and its metabolites, glycidol and beta-chlorolactic acid, in the in vitro comet assay on CHO cells. Our results show the absence of genotoxic potential of 3-MCPD in vivo in the target as well as in the non-target organs. Glycidol, the epoxide metabolite, induced DNA damages in CHO cells. beta-Chlorolactic acid, the main metabolite of 3-MCPD in rats, was shown to be devoid of DNA-damaging effects in vitro in mammalian cells.

3-Monochloropropane-1,2-diol (3-MCPD) is a food processing contaminant in a wide range of foods and ingredients and is a suspected cause of cancer. In this study, the 13-week toxicity of 3-MCPD was examined in B6C3F1 mice (10/sex/group) administered 3-MCPD doses of 0, 5, 25, 100, 200 and 400 ppm dissolved in their drinking water over a 13-week period. All the mice survived to the end of study. The mean body weight gains in the males and females given 400 ppm were significantly lower than those of the controls. The relative kidney weights of the males and females given 200 and 400 ppm were significantly higher than those of the controls without any corresponding histopathological changes. The sperm motility was lower in the 400 ppm group than the control, and there was a significant increase in the incidence of germinal epithelium degeneration in the 200 and 400 ppm groups. A delayed total estrus cycle length was observed in the 400 ppm group without any histopathological changes. Based on these results, the target organ was determined to be kidney, testis, and ovary. The no-observed-adverse-effect level (NOAEL) was found to be 100 ppm (18.05 mg/kg/day for males and 15.02 mg/kg/day for females).

Very recently, 3-hydroxy-4-[(E)-(2-furyl)methylidene]methyl-3-cyclopentene-1,2-dione (1) has been successfully identified as an intensively coloured Maillard product formed from glucose and L-proline upon thermal food processing. Using a biomimetic synthetic strategy, reference material of compound 1 was prepared and purified, and then used to study its effect on the growth of human tumor cells. Compound 1 was found to potently inhibit the growth of human tumor cells in vitro. Using a reporter gene assay we could show that in growth inhibitory concentrations compound 1 effectively inhibits the phosphorylation of the transcription factor Elk-1. In addition, 1 was found to affect the microtubule skeleton. The human mammary carcinoma cell line MCF-7 exhibits a decrease of the microtubule organisation when treated for 24 h with 1 (> or =20 microM). At concentrations of 30 microM and above a loss of microtubule integrity is observed after 1 h incubation. In vitro studies demonstrated that the polymerisation and, to a minor extent, also the depolymerisation of tubulin, isolated and purified from bovine brain, is inhibited in a dose-dependent manner at concentrations of 30 microM and above. This is the first time that a non-enzymatically formed browning compound of known structure was reported to effectively inhibit tumor cell growth and microtubule assembly.

The effect of black tea polyphenols on 1,2-dimethylhydrazine (DMH)-induced oxidative DNA damage in rat colon mucosa has been investigated. Fischer 344 rats were treated orally with thearubigin (TR) or theafulvin (TFu) for 10 days (40 mg/kg), injected ip with DMH (20 mg/kg) or saline and sacrificed 24 hr after DMH administration. The levels of 8-hydroxy-2'-deoxyguanosine (8-OHdG) were measured in colonic mucosa DNA and expressed as a ratio relative to 2'-deoxyguanosine (2dG). Control rat mucosa had 8-OHdG values of 1.12 +/- 0.14/10(5) dG (mean +/- SEM, n=11), whereas DMH-treated rats significantly higher values (1.52 +/- 0.14/10(5) dG, n=26, P<0.05). Pretreatment of rats with TR had significantly inhibited DMH-induced oxidative DNA damage 0.99 +/- 0.09/10(5) dG, n=10, P<0.05) and a similar, although less marked, effect was observed with TFu (1.15 +/- 0.19/10(5), n=9, P=0.06). These findings confirm that DMH causes oxidative DNA damage in the colon mucosa of rats and demonstrate that this effect is prevented by the consumption of complex polyphenols from black tea.

Coumarin (1,2-benzopyrone), a natural dietary constituent and drug currently under evaluation for treatment of certain cancers and lymphedema, reduces polycyclic aromatic hydrocarbon-induced neoplasms in rodents. Because most rodents metabolize coumarin through 3,4-epoxidation, whereas 7-hydroxylation predominates in humans, their suitability as a model for coumarin effects in humans has been questioned. We examined coumarin chemoprotection against the promutagen and dietary contaminant aflatoxin B1 with human liver S9 bioactivation in the Chinese hamster ovary cell/hypoxanthine-guanine phosphoribosyltransferase mutation assay. Coumarin in the absence of aflatoxin B1 was not mutagenic or cytotoxic up to 500 microM. When included with either 1 or 10 microM aflatoxin B1, coumarin produced a dose-dependent increase in mutant frequency and cytotoxicity. At concentrations greater than 50 microM, coumarin stimulated human liver S9 bioactivation of aflatoxin B1 to the mutagenic 8,9-epoxide. This increase was 12- and fivefold at 500 microM coumarin with 1 and 10 microM aflatoxin B1, respectively, compared with incubations with aflatoxin B1 alone. These findings differ from previous results with liver S9 from other species, and indicate that coumarin co-mutagenicity with aflatoxin B1 and human liver S9 is through increased aflatoxin B1 bioactivation.

Indole-3-carbinol (I-3-C) and 5,10-dihydroindeno[1,2-b]indole (DHII) have been shown to be protective against carbon tetrachloride and other chemicals that cause hepatic toxicity. In part, this protection appears to be afforded by the ability of these compounds to act as antioxidants, with DHII having much the greater efficacy. In order to understand the mechanisms of chemoprotection, as well as the potential for therapeutic and pharmaceutical use in humans, the antioxidants I-3-C and DHII were examined for their intrinsic acute toxicity, and their hepatic enzyme inducing properties in mice. The results were compared with those of the well characterized agent phenobarbital. Following treatment by gavage for 10 days with 50 mg compound/kg body weight, I-3-C produced modest (10-50%) increases in hepatic cytochrome P-450, aminopyrine N-demethylase, UDP-glucuronosyl transferase (UDPGT) and glutathione S-transferase (GST), and a four-fold increase in NAD(P)H: (quinone acceptor) oxidoreductase (quinone reductase) activity. DHII did not alter oxidative enzyme activities, but increased GST and UDPGT by about 50%, and quinone reductase over five-fold. In the acute toxicity studies, DHII produced no observable 24-hr acute toxicity up to 4 g/kg body weight, except for a slight decrease in haematocrit. However, I-3-C exhibited a dose-dependent toxicity above 100 mg/kg body weight, including a decrease in hepatic reduced glutathione after 2 hr and severe neurological toxicity, and the release of liver enzymes to the plasma at 24 hr. We conclude, on the basis of the superior antioxidation efficacy of DHII, its enzyme-inducing properties, and intrinsic toxicity, that DHII or cogeners thereof have great potential as chemoprotective or therapeutic agents. However, I-3-C does not have such potential.

The influence of 5,10-dihydroindeno[1,2-b]indole (indenoindole) on carbon tetrachloride (CCl4)-mediated hepatotoxicity and lipid peroxidation were examined. Indenoindole (25 mg/kg body weight) ameliorated the increase in liver enzymes appearing in the plasma 24 hr after CCl4 administration, with about a 63% reduction for alanine transaminase, 56% for ornithine transcarbamylase and 84% for alkaline phosphatase. Indenoindole also partially prevented, in a dose-dependent fashion, the decrease in hepatic cytochromes P-450, total tissue reducing equivalents and hepatic ascorbate levels resulting 4 hr after CCl4 administration. In a homogeneous chemical system consisting of purified soybean phospholipid substrate in chlorobenzene, azobisisobutyronitrile-initiated lipid peroxidation was inhibited by indeno-indole, with 50% inhibition occurring at about 17 microM. Inhibition by indenoindole of iron-ascorbate-initiated lipid peroxidation in aqueous buffer containing phospholipid vesicles was about tenfold more efficient, with 50% inhibition occurring at about 1.5 microM. Presumably, this was due to the increased concentration of indenoindole in the membrane of the phospholipid vesicle. The efficiency of inhibition of lipid peroxidation was in the order of indenoindole = butylated hydroxytoluene (BHT) greater than alpha-tocopherol much greater than indole greater than indene. These 50% inhibition values of lipid peroxidation for these compounds were similar in an assay system composed of NADPH-fortified mouse-liver microsomes initiated with CCl4. For indenoindole, the 50% inhibition value (1.3 microM) was more than two orders of magnitude less than the spectral binding constant for indenoindole to mouse-liver cytochrome P-450 (Kd = 236 microM), implying that the partial inhibition of metabolic activation of CCl4 was not responsible for the inhibition of lipid peroxidation observed with indenoindole in this system. It appears that indenoindole may trap reactive radicals and inhibit lipid peroxidation in vitro. Regardless of whether inhibition is at the level of scavenging CCl4 metabolite radicals, or lipid radicals in membranes, radical trapping provides a plausible mechanism by which this compound inhibited CCl4 hepatotoxicity.

Acute toxicologic and neurotoxic effects were evaluated in Fischer 344 rats exposed to 0, 50, 200, 600, or 2000 ppm 1,2-dichloroethane (ethylene dichloride; EDC) for 4 h or 0, 50, 100 or 150 ppm for 8 h. Neurobehavioral and neuropathologic effects were assessed using a functional observational battery (FOB; baseline, days 1, 8, and 15), and by light microscopy, respectively. Acute toxicologic effects were assessed by bronchoalveolar lavage (BAL) and histopathology of the respiratory tract and selected target organs. Neurobehavioral effects consistent with central nervous system (CNS) depression were present at concentrations >200 ppm and were restricted to day 1. There were no neuropathologic changes in the CNS, however, olfactory epithelial regeneration 15 days after exposure to > or = 200 ppm was observed. The no-observed-effect concentration (NOEC) for behavioral neurotoxicity was 200 ppm EDC for 4 h. There were no effects on BAL parameters in any exposure group. Exposure to 2000 ppm EDC altered adrenal gland, kidney, and liver weights, and resulted in morphologic alterations in the kidney and liver. Degeneration/necrosis of the olfactory epithelium was observed at > or = 200 ppm for 4 h and > or = 100 ppm for 8 h. Based on olfactory epithelial degeneration/necrosis, the most sensitive indicator of toxicity in this study, the overall NOEC was 50 ppm EDC for up to 8 h in rats.

In some US potable water supplies, 1,2,3-trichloropropane (TCP) has been present at ranges of non-detect to less than 100 ppb, resulting from past uses. In subchronic oral studies, TCP produced toxicity in kidneys, liver, and other tissues. TCP administered by corn oil gavage in chronic studies produced tumors at multiple sites in rats and mice; however, interpretation of these studies was impeded by substantial premature mortality. Drinking water equivalent levels (DWELs) were estimated for a lifetime of consumption by applying biologically-based safety/risk assessment approaches, including Monte Carlo techniques, and with consideration of kinetics and modes of action, to possibly replace default assumptions. Internationally recognized Frameworks for human relevance of animal data were employed to interpret the findings. Calculated were a reference dose (=39 microg/kg d) for non-cancer and Cancer Values (CV) (=10-14 microg/kg d) based on non-linear dose-response relationships for mutagenicity as a precursor of cancer. Lifetime Average Daily Intakes (LADI) are 3130 and 790-1120 microg/person-d for non-cancer and cancer, respectively. DWELs, estimated by applying a relative source contribution (RSC) of 50% to the LADIs, are 780 and 200-280 microg/L for non-cancer and cancer, respectively. These DWELs may inform establishment of formal/informal guidelines and standards to protect public health.