Search

MA is a chemical intermediate, manufactured and processed within closed systems. While so far available subacute to chronic inhalation toxicity studies performed in compliance with OECD TG principles gave no indication of any carcinogenic potential for MA, a recent 2-year inhalation study with F344/DuCrlCrlj rats published in 2017 by the JBRC showed a statistically significant increase of squamous cell carcinoma in the nasal cavity of male rats at the highest tested concentration of 160 ppm. However, the results of the different studies in total indicate that this high concentration exceeded the MTC. As MA has a low potential for genotoxic and mutagenic activity, the increased tumour incidence can be attributed to a non-genotoxic mechanism, namely to a strong inflammatory response observed in this study. Together with mechanistic and epidemiologic data for other compounds related to nasal carcinogenesis via this mode of action, it can be concluded that the relevance of this increased tumour incidence in male rats for humans is questionable. Also, a long-term exposure to higher concentrations of MA is highly unlikely to be reached in the environment or at workplaces. Therefore, a risk for humans including cancer hazard is considered implausible.

In this study, the acute (72 h and 14 d) and chronic (28 d and 8 weeks) effects of cyfluthrin on earthworms were evaluated across different endpoints, which are mortality, growth, reproduction and enzyme activities. Cyfluthrin was rated as moderately toxic in 72-h filter paper test and low toxic in 14-day soil test. The exposure of earthworms to cyfluthrin-polluted soil for 8 weeks showed that growth of earthworms was inhibited by cyfluthrin, cocoon production and hatching were inhibited by 20–60 mg/kg cyfluthrin. Moreover, 28-day soil test on the responses of enzymes associated with antioxidation and detoxification showed that the activities of catalase (CAT) and glutathione S- transferase (GST) were initially increased by cyfluthrin at 5–20 mg/kg, but reduced at 30–60 mg/kg, peroxidase (POD) was increased by 26–102% by cyfluthrin in the early period, except 5 mg/kg on day 7, and ethoxyresorufin-O-deethylase (EROD) was increased by 29–335% by cyfluthrin after 3 days. Cyfluthrin degraded with a half-life of 24.8–34.8 d, showing the inconsistency between the continuous toxic responses of earthworms and degradation of cyfluthrin in soil. The variable responses of these indexes indicated that different level endpoints should be jointly considered for better evaluation of the environmental risk of contaminants in soil.

In genetic toxicology, risk assessment has traditionally adopted linear dose-responses for any compound that causes genotoxic effects. Increasing evidence of non-linear dose-responses, however, suggests potential cellular tolerance to low levels of many genotoxicants with diverse modes of action. Such putative non-linear dose-responses need to be substantiated by strong mechanistic data that identifies the mechanisms responsible for the tolerance to low doses. This can be achieved by experimental demonstration of cytoprotective mechanisms and by providing experimental support for the existence of tolerance mechanisms against low dose effects. By highlighting key experiments into low dose mechanisms, this review aims to clarify which mechanistic data are required to support the use of non-linear dose-response models in risk assessment. Such key experiments are presented and discussed for alkylating agents, oxidants, particulate matter, nucleoside analogues, topoisomerase inhibitors and aneugens and exemplify the use of gene knockout models or transgenic models as well as chemical modulators of key effectors of relevant pathways and their impact on dose-response relationships. In vitro studies are particularly valuable to elucidate mechanisms of low-dose protection or lack thereof, while in vivo experiments are most appropriate for deriving a safe dose. In order to evaluate the existence of non-linear dose-response relationships for genotoxicants, we suggest that careful attention should be given to the mode of genotoxic action, relevant biomarkers of exposure, as well as to the existence and impact of potential cytoprotective mechanisms like detoxifying metabolism and DNA repair.

2-Acetylaminofluorene (AAF) is a complete carcinogen in rat liver. The genotoxic effects of reactive metabolites are considered necessary but not sufficient to explain tumor formation. An overview is given of an AAF-feeding experiment designed to demonstrate early effects, preceding the development of enzyme-altered foci to support the hypothesis that toxic effects lead to a cirrhosis-like transformation as a prerequisite for the expansion of initiated foci and how those effects influence the dose-time-response relationship of tumor formation. Male Wistar rats were fed 0.005, 0.01, 0.02, 0.04 and 0.08% AAF in the diet for 2, 4, 8, and 16 weeks. GST-P-positive foci developed more than proportionately only at 16 weeks. As a first sign of morphological alterations the number of apoptoses increased (2 weeks), the proliferation rate followed with some delay and was maximal at 4 weeks. The most sensitive parameter for adaptive responses was the inhibition of the mitochondrial permeability transition, studied ex vivo. All parameters increased dose-dependently at low doses. A threshold could not be detected, but effects developed much more gradually with the lowest, non-toxic dose. The situation of massive development of foci observed with the higher doses at 16 weeks was not reached. Apoptosis and proliferation rate reach a plateau between 4 and 8 weeks with some of the doses indicating a period in which some balance between adaptation and stress response exists.

Caffeic acid (CA, 3,4-dihydroxycinnainic acid), at 2% in the diet, had been shown to be carcinogenic in forestomach and kidney of F344 rats and B6C3F1 mice. Based on its occurrence in coffee and numerous foods and using a linear interpolation for cancer incidence between dose 0 and 2%, the cancer risk in humans would be considerable. In both target organs, tumor formation was preceded by hyperplasia, which could represent the main mechanism of carcinogenic action. The dose-response relationship for this effect was investigated in male F344 rats after 4-week feeding with CA at different dietary concentrations (0, 0.05, 0.14, 0.40, and 1.64%). Cells in S-phase of DNA replication were visualized by iminunohistochemical analysis of incorporated 5-bromo-2′-deoxyuridine (BrdU), 2 hr after intraperitoneal injection. In the forestomach, both the total number of epithelial cells per millimeter section length and the unit length labeling index of BrdU-positive cells (ULLI) were increased, about 2.5-fold, at 0.44) and 1.64%. The lowest concentration (0.05%) had no effect. At 0.14%, both variables were decreased by about one-third. In the kidney, the labeling index in proximal tubular cells also indicated a J-shaped (or U-shaped) dose response with a 1.8-fold increase at 1.64%. In the glandular stomach and in the liver, which are not target organs, no dose-related effect was seen. The data show a good correlation between the organ specificity for cancer induction and stimulation of cell division. With respect to the dose-response relationship and the corresponding extrapolation of the animal tumor data to a human cancer risk, a linear extrapolation appears not to be appropriate

2-Acetylaminofluorene (AAF) is one of the most widely studied model carcinogens. It produces liver tumors in rats. Comparison with other arylamides shows that promutagenic DNA lesions are necessary but not sufficient to explain this tissue-specific effect. Mutagenicity of AAF was studied in AS52 cells and compared with that of 2-acetylaminophenanthrene and trans-4-acetylaminostilbene which are incomplete carcinogens in rat liver. The major mutations were G to T transversions in all cases. All three acetamides acted as initiators in an initiation–promotion experiment with phenobarbital as a promoter. Chronic toxic effects of AAF were attributed to specific effects of AAF metabolites on mitochondrial respiration. Electron drainage by 2-nitrosofluorene causes an uncoupling effect on oxidative phosphorylation in vitro. Corresponding compensatory effects were observed in vivo. Initiating as well as promoting properties of AAF are therefore considered responsible for the generation of rat liver tumors. The results support the hypothesis that genotoxic effects generate initiated cells which begin to proliferate only when microcirculation is disturbed due to cirrhotic alterations. These are triggered by non-genotoxic interference with mitochondrial respiration and oxidative phosphorylation.

The genotoxic effects of 2-acetylaminofluorene (AAF) alone cannot explain the formation of rat liver tumors. It has been proposed that mitochondrial effects are associated with its tumor-promoting properties. These mitochondrial effects are thought to trigger apoptosis and regenerative proliferation, which alters the liver lobule in a cirrhosis-like manner. A situation is generated which favors the growth of initiated cells. To test this sequence of events, the dose dependence of early effects with time was studied. Male Wistar rats received 50, 100, 200, 400, or 800 ppm AAF in the diet and the following endpoints were analyzed at 2, 4, 8, and 16 weeks of feeding: apoptotic cell death, cell proliferation, GST-P-positive foci (placental form of glutathione S-transferase), and morphological alterations. Hydrolyzable hemoglobin adducts were used as a dosimeter for metabolic activation after 2 weeks of feeding. The hemoglobin adduct levels increased linearly with dose. With the conventional carcinogenic concentration of 200-ppm AAF in the diet, the number of apoptoses increased first, predominantly in the periportal area (2 weeks). Cell proliferation followed with some delay (4 weeks). This reflects regenerative tissue response and not the growth of initiated cells, because the number of enzyme-altered foci was still extremely low at that time. Foci developed only later when the morphology had changed. With 50 ppm AAF in the diet, a no-effect level had not been reached for any of the endpoints, but foci developed much more gradually than with higher doses. Unexpectedly, the proliferative response stabilized at 8 weeks with a labeling index of 12-17, with all AAF concentrations. The observed sequence of events supports the hypothesis. It is concluded that (1) The proliferation of initiated cells-defined as promotable cells-is largely determined by the cellular environment, such as morphologically altered liver. (2) The morphological alterations in rat liver result from imperfect regeneration from toxic effects. (3) Imperfect regeneration results from limitations in the possibilities to adapt to chemical stress. (4) If these limits are overwhelmed and morphology has changed to a certain extent, preneoplastic foci develop; this occurs much faster, at least, than without these changes.

In the present study we investigated c-fos expression in rat livers, that was initiated with the three arylamines, 2-acetylaminofluorene, 2-acetylaminophenanthrene and trans-4-acetylaminostilbene. The tumor promoter phenobarbital was applied chronically for 26, 52 and 100 weeks. Gene expression, determined by the mRNA level, and FOS protein were increased after 52 weeks of treatment in arylamine initiated as well as in phenobarbital only treated animals. Expression of c-fos seems to be a phenobarbital induced effect that is independent of additional initiator treatments. This finding was supported by immunohistochemical studies demonstrating increased FOS levels to be localized around the central vein. The results indicate that phenobarbital, a widely used tumor promoter, induces c-fos expression. In addition, we demonstrated enhanced FOS in GST-P-positive foci and in tumors.

The tumour promoting properties of carcinogenic 2-acetylaminofluorene (AAF) in rat liver are essentially unknown. We proposed that mitochondria are a target for the cytotoxic effects of 2-nitrosofluorene (NOF), a metabolite of AAF, since NOF induces a redox-cycle at complex I and complex III of the respiratory chain, and impairs respiration and oxidative phosphorylation. We now demonstrate that NOF is a potent inducer of the mitochondrial permeability transition pore (PTP) in isolated mitochondria. In the presence of Ca2+, NOF induced rapid swelling of mitochondria in a dose-dependent manner and depolarized the mitochondrial membrane. Permeability transition as well as depolarization were abolished completely by pre-incubation with the PTP inhibitor cyclosporin A. To study whether the PTP is involved in in vivo toxicity, rats were fed a diet containing AAF (0.04%) for 2 weeks. After isolation of mitochondria, permeability transition was induced by high Ca2+ concentrations (150-400 microM) or phosphate plus Ca2+. Swelling was determined as maximal rate of absorption decrease at 540 nm (delta A/delta t). Surprisingly, delta A/delta t-values of mitochondria from AAF-fed rats were significantly lower (16.3 +/- 4.8 x 10(3)/min) than of mitochondria from control animals (32.7 +/- 4.1 x 10(3)/min; P < 0.02). In the presence of phosphate (15 mM), delta A/delta t-values of mitochondria from AAF-fed rats were even lower (10% of control). Moreover, the membrane potential which was dissipated rapidly by the PTP-inducer NOF (30 microM) at a Ca2+ concentration of 80 microM in mitochondria from control animals, remained constant in mitochondria of AAF-treated rats. We therefore propose that the regulation of the PTP is altered on chronic AAF-feeding. The increased resistance of mitochondria against permeability transition may alter the threshold for apoptosis and thus suppress apoptosis. We also discuss the role of epigenetic modifications in early stages of carcinogenesis.

2-Acetylaminofluorene (2-AAF) is a complete carcinogen in rat liver. To investigate the specific properties, that distinguish 2-AAF from incomplete carcinogens, rats were fed 0.02% AAF in the diet for 6, 12, 16 weeks and some indicators of genotoxic and chronic toxic effects were studied immunohistochemically. GST-P, a marker for single initiated cells and preneoplastic foci, was induced in response to 2-AAF exposure. The effects were slight after 6 weeks of feeding, after 12 weeks GST-P-positive preneoplastic foci were present. The proto-oncogenes c-fos and c-jun are induced by several tumor promoters. In the present study c-FOS protein levels were increased in all 2-AAF treated animals at early stages not only in preneoplastic foci. However, all GST-P-positive foci were also c-FOS-positive. Surprisingly c-JUN was not enhanced in GST-P positive foci. It was comparatively expressed in hepatocytes and bile duct cells in all animals. We did not observe any immunolabeling for p53, either in preneoplastic foci or in hepatocytes from treated animals. A significant increase of apoptoses was noted in the whole liver lobule but also gathered in groups in the periportal area. The results support our proposal that oxidative stress and energy impairment in the mitochondria of periportal hepatocytes trigger morphological alterations in the rat liver.

Liver tumors were generated in Wistar rats in an initiation-promotion experiment. 2-Acetylaminofluorene (AAF), 2-acetylaminophenanthrene (AAP), and trans-4-acetylaminostilbene (AAS) were administered to newborn animals as initiators, and phenobarbital as a promoter was added to the drinking water after weaning. Livers were examined after 26, 52, 78, and 104 weeks. Tumors were present in all groups except for at the first time point. The potency of the initiators decreased in the order AAS > AAP > AAF. DNA from tumors of all groups and of control livers was analyzed for mutations in the H-ras gene, but no mutations could be found. The sequence of almost the entire H-ras gene was determined and was compared to other H-ras genes. There are some differences with the sequence in other rat strains, particularly in intron D containing the alternative splicing site. The expression of the H-ras gene has also been studied by various methods in enzyme altered foci and tumors, but no alterations could be found. It is, therefore, concluded that structural of functional alterations of this proto-oncogene are not involved in the generation of liver tumors in Wistar rats by the three genotoxic arylamines.

The mouse spot test, an in vivo mutation assay, has been used to assess a number of chemicals. It is at present the only in vivo mammalian test system capable of detecting somatic gene mutations according to OECD guidelines (OECD guideline 484). It is however rather insensitive, animal consuming and expensive type of test. More recently several assays using transgenic animals have been developed. From data in the literature, the present study compares the results of in vivo testing of over twenty chemicals using the mouse spot test and compares them with results from the two transgenic mouse models with the best data base available, the lacI model (commercially available as the Big Blue® mouse), and the lacZ model (commercially available as the Muta™ Mouse). There was agreement in the results from the majority of substances. No differences were found in the predictability of the transgenic animal assays and the mouse spot test for carcinogenicity. However, from the limited data available, it seems that the transgenic mouse assay has several advantages over the mouse spot test and may be a suitable test system replacing the mouse spot test for detection of gene but not chromosome mutations in vivo.

As part of a larger literature study on transgenic animals in mutagenicity testing, test results from the transgenic mutagenicity assays (lacI model; commercially available as the Big Blue® mouse, and the lacZ model; commercially available as the Muta™Mouse), were compared with the results on the same substances in the more traditional mouse bone marrow micronucleus test. 39 substances were found which had been tested in the micronucleus assay and in the above transgenic mouse systems. Although, the transgenic animal mutation assay is not directly comparable with the micronucleus test, because different genetic endpoints are examined: chromosome aberration versus gene mutation, the results for the majority of substances were in agreement. Both test systems, the transgenic mouse assay and the mouse bone marrow micronucleus test, have advantages and they complement each other. However, the transgenic animal assay has some distinct advantages over the micronucleus test: it is not restricted to one target organ and detects systemic as well as local mutagenic effects.

Applying labelled phenylalanine or tyrosine to purified intact spinach chloroplasts, only the corresponding phenylacetic acids but not the cinnamic acids could be detected. The addition of mercaptoethanol or dl-dithiothreitol and the variation of light conditions had only a slight effect. However, cinnamic acids could be found together with phenylacetic acids in leaf homogenates indicating the presence of phenylalanine and/or tyrosine ammonia lyase outside the spinach chloroplasts. Similar results were obtained with barley leaf homogenates, where cinnamic acids were the main products. Reviewing recent findings on amino acid synthesis in spinach leaves, it may be concluded that the synthesis of aromatic amino acids is restricted to the chloroplast, whereas the metabolism of secondary aromatic compounds is predominantly localized outside the chloroplasts.