Benzene and five of its known metabolites-muconic acid, hydroquinone, catechol, p-benzoquinone, and benzentriol-were examined For DNA damage in human lymphocytes using the alkaline Comet essay, and conditions were optimised to determine responses. Metabolic activation (S-9 mix) was included in the assay for varying times to try to enhance effects. In addition, the effects of catalase were investigated as if is known to be present in S-9 mix reducing oxidative damage, and some benzene metabolites are known to react through oxygen radical mechanisms. Effects were also examined in cycling cells to determine whether they were more sensitive to damage then noncycling cells. Comets were measured either by eye or by image analysis. Data have been presented according to length of treatments.When Comets were measured by eye after treatment with hydrogen peroxide (H2O2), the positive control, and each compound for 0.5 hr, only H2O2 and benzenetriol induced pronounced DNA damage without metabolic activation. The effect of catechol was moderate compared with that of benzenetriol. There was a very weak effect of benzene in the absence of rat liver S-9 mix. In the presence of S-9 mix, benzene was not activated. The effect of benzenetriol was greatly reduced by the external metabolising system, but p-benzoquinone became activated to some extent. Catalase abolished the effect of benzenetriol, suggesting that H2O2 formed during autoxidation may be responsible for the DNA-damaging ability of this metabolite. The presence of catalase in S-9 mix may explain the detoxification of benzenetriol and the failure to defect consistent benzene responses. Mitogen-stimulated cycling cells were less sensitive to H2O2 and benzenetriol than unstimulated G(O) lymphocytes.When comets were measured by image analysis, a 0.5-hr treatment with H2O2 and benzenetriol and catechol confirmed results analysed by eye, with S-9 mix greatly reducing responses. When treatments were increased to 1 hr in the presence and absence of S-9 mix, benzene at a 5-fold increased dose produced a significant positive response but not at the lower dose. When treatment times were increased to 2 and 4 hr, doses were also increased, and muconic acid, hydroquinone, catechol, and benzoquinone in the presence of S-9 mix showed positive time and dose-related responses, and at the highest dose of benzoquinone the morphology of the nucleus was affected. Effects tended to become more pronounced at high doses and after longer exposures, although this was not always consistent from experiment to experiment.In conclusion, benzene and all metabolites investigated gave positive responses. Where altered responses were observed, they were significantly different from the corresponding controls. (C) 1995 Wiley-liss, Inc.

The well known and previously widespread insecticide lindane has been re-assessed for DNA-damaging activity. A first group of investigations using standard in vitro and in vivo mutagenicity assays did not indicate any genotoxic effects of lindane at all. The assay systems used were for the induction of HPRT mutations and sister chromatid exchanges in CHO cells cultured in vitro, and for micronuclei induction in vivo in bone marrow cells of rats, hamsters and mice. Also, lindane was assessed for its potential to induce sister chromatid exchanges in vivo in the bone marrow of Chinese hamsters. These specific assay systems had not been used previously for elucidating the genotoxic effects of this compound, but they are basically similar to other standard mutagenicity assays in which lindane has been shown to be devoid of genotoxic activity. The second part of the investigations was directed at re-evaluating a previously reported positive effect of the compound in primary rat hepatocytes in vitro. We performed in vitro and in vivo studies with hepatocytes from the rat liver and used alkaline elution to detect DNA damage. However, we could not demonstrate that lindane induced genotoxicity, unless considerable concomitant cytotoxicity was apparent as well. Finally, since lindane can be ingested and inhaled by humans, we also measured the induction of DNA damage in local target organs of absorption using single cell microgelelectrophoresis (the comet assay). In these cases lindane was genotoxic in cells of the gastric and nasal mucosa in vitro and also in vivo following appropriate routes of application (oral and inhalational exposure).

An acknowledged weakness of current testing programmes for genotoxic hazard has been the potential insensitivity of the established mouse bone marrow micronucleus test and rat liver unscheduled DNA synthesis (UDS) assays to direct-acting or short-lived mutagens, which may be consumed at the site of initial contact. In such cases, in vivo test systems sampling tissues such as the skin or the stomach would provide valuable data. To test these principles a stomach UDS assay was evaluated using the potent locally active mutagen 1-chloromethylpyrene (1-CMP). Contrary to expectations, no UDS response was observed 16 h following 1-CMP dosage by oral gavage. To confirm the integrity of the 1-CMP used for the stomach UDS assay, a sample of the stored chemical was re-evaluated in vitro and shown to be still strongly positive in the Ames assay and to have alkylating activity at least 15 min after incubation at stomach acid pH. No UDS response was observed when test dose levels were reduced or when earlier sampling times were used. Other genotoxic endpoints were examined in stomach. 32P-Postlabelling analysis revealed high levels of adduct formation in gastric DNA. An assay utilizing electrophoresis of DNA (the comet assay) showed the occurrence of DNA damage following dosing with 1-CMP in vivo. These positive results confirmed that 1-CMP should be regarded as a potential in vivo genotoxin. The failure to detect a UDS response to 1-CMP in stomach was investigated; a strong UDS response was observed in an in vitro hepatocyte UDS assay of 1-CMP indicating that the rat was capable of repairing 1-CMP-derived DNA adducts. Pretreatment of rats with hydroxyurea depressed the level of incorporation of thymidine into DNA both in negative and positive [methyl-N-nitrosoguanidine (MNNG)] controls. The results of these studies indicated that the protease digestion method employed did not selectively or efficiently sample those cells with any UDS response to 1-CMP or MNNG, and the activity seen for the latter was most likely due to the presence of S phase cells within the digests. As a result of the finding that UDS responses were not demonstrated for the potent direct-acting mutagens 1-CMP and MNNG, the protease digestion/scintillation method for stomach UDS does not appear to have general value in a screening programme for locally active genotoxic agents.

The methylating agent streptozotocin is active in the mouse bone marrow micronucleus assay following a single intraperitoneal injection of 150 - 180 mg/kg. This correlates with its previously reported toxicity to mouse germ cells when administered by the same route of exposure. The potent mutagenicity of streptozotocin to strain G46 of Salmonella typhimurium is compared with its much weaker activity in strain TA1535. The genotoxicity of streptozotocin in vivo is reviewed.

We report the results of a collaborative study for the detection of chemical-induced DNA damage in primary cultures of rat hepatocytes. The methods include the detection of unscheduled DNA synthesis (UDS) with either autoradiography (5 laboratories) or liquid scintillation counting (2 laboratories) and the assessment of DNA single-strand breaks with the alkaline elution assay (1 laboratory). Interlaboratory standardization was omitted in order to prove the agreement of the assays under routine conditions. Five coded chemicals were tested. For 4 chemicals (2-acetylaminofluorene, thiourea, glycerine and potassium chloride) the UDS data were consistent in all laboratories, thus indicating a high consensus of the test systems applied in the different laboratories. Those 3 chemicals that were not expected to elicit genotoxic activity (thiourea, glycerine, and potassium chloride) yielded negative results in all laboratories. 2-Acetylaminofluorene, a known DNA-damaging agent in hepatocytes, gave strongly positive responses in all laboratories. In contrast, N-nitrosodiphenylamine led to equivocal responses.

1. The in vitro studies showed that organ specific metabolic activation does not appear to play a predominant role for the in vivo activities of the studied nitrosamines 2. The in vivo studies following 1 h exposure of rats with the nitrosamines can differentiate between organs susceptible for genotoxicity and and those which are not. Nontarget organs in carcinogenicity can not be identified exclusively. 3. The additional study of persistence of genotoxicity may identify organs susceptible for carcinogenicity. Presently, we are working on new techniques to detect DNA SSB and other events with microscale methods. This is necessary to allow a more complete elucidation of genotoxicity in remote target organs and with other carcinogens which may not induce DNA SSB. Accordingly in the near future we expect to have even more versatile tools available to study toxicokinetics of foreign compound. Meanwhile our work with N-nitrosamines is continuing in order to better understand their in vivo modes of action and to better evaluate their burden and risk for man.

Di(2-ethylhexyl)phthalate (DEHP) is a widespread environmental contaminant with potential toxic and carcionogenic effects. Although the biological action of DEHP has been a subject of intense study, the question of whether or not it poses a substantial human hazard still remains unanswered (Reddy and Lalwai 1983). In this regard species- and dose-related differences in responses to DEHP action appear important (Albro et al. 1982). So far the carcinogenicity of DEHP has only been demonstrated in rats and mice by giving very high doses (NTP 1982). The low order of acute toxicity and the lack of consistent pathological findings at low doses delineate other aspects of DEHP action. Still little is known about subtle DEHP effects that may be induced by the level of the expected environmental exposure (NTP 1981). In an attempt to describe subtle changes and recognize species-related differences, we applied image analysis to hepatocyte nuclei of rats and hamsters treated by single doses of DEHP.