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More emphasis should be placed upon using biomarkers to address potential health risk among populations exposed to high concentrations of environmental toxicants. Among these studies, those which integrate exposure measurements with analyses of validated biomarkers may provide more reliable information for risk assessment and disease prevention. We have used a multidisciplinary approach to elucidate potential health hazards in a population living around uranium mining/milling facilities. The study included 24 target and 24 control residents who were matched for age and gender and selected based on time of residence in the study areas and proximity to mining/milling sites. Environmental samples were analyzed for uranium-238 (238U) concentrations and lead isotope ratios using inductively coupled plasma-mass spectrometry (ICP-MS) procedures, and blood samples were collected for cytogenetic analysis. We found that the 238U concentrations in soil samples were significantly higher than those in the control areas. In addition, the concentrations in the surface soil were significantly higher than in the subsurface soil (p<0.05) from target areas indicating environmental contamination by the mining/milling activities. Lead isotope data from soil samples taken near a railroad transfer location was significantly different from those of other sites, indicating contamination by non-native ore transported from sources outside of the region to local milling facilities for processing. Therefore, local residents have been exposed to low levels of radioactive contamination from the mining/milling activities on a daily basis for many years. From our cytogenetic analysis, the target population had more chromosome aberrations than the controls, although the differences were not significant (p<0.05). However, using our challenge assay, cells from the target population had a significantly abnormal DNA repair response, compared to cells from the same control population. In conclusion, the observed environmental contamination by uranium is consistent with the observed genotoxic effects in the target residents. Therefore, the residents have increased health risk and some of the health problems will most likely be related to exposure to the radioactive contaminants. Since the chromosome aberration frequency revealed increased, but not significant differences between the exposed and the control populations, we conclude that the health risk among the exposed residents is similar to those among nuclear workers., (Copyright 1998 Elsevier Science B.V.)

Benzene is a widely used chemical and common environmental contaminant. It is carcinogenic in man and animals and is genotoxic in mice, rats, and occupationally exposed humans at doses above one part per million. In order to evaluate the genotoxic effects of prolonged exposures to very low concentrations of benzene, we exposed CD-1 mice to benzene by inhalation for 22 h per day, seven days per week for six weeks at 40, 100 and 1000 parts per billion (ppb). Additional groups were exposed to purified air or were housed in standard plastic cages. The effects of in vivo exposure to benzene were evaluated by using an autoradiographic assay to determine the frequency of mutants which represent mutations at the hypoxanthine-guanine phosphoribosyl transferase (hprt) locus in spleen lymphocytes. At the end of the six weeks exposure period lymphocytes were recovered from the spleens of the mice and cryopreserved prior to assay. Mutant cells were selected on the basis of their ability to incorporate tritiated thymidine in the presence of 6-thioguanine. The weighted mean variant (mutant) frequencies (Vf) of female mice (three per group) were 7.2 x 10(-6) at 0 ppb; 29.2 x 10(-6) at 40 ppb; 62.5 x 10(-6) at 100 ppb and 25.0 x 10(-6) at 1000 ppb. The Vf of unexposed mice housed in standard cages was 13.2 x 10(-6). In male mice the same pattern of response was observed, but the increases in Vf in response to benzene were not as great. In both sexes of mice, the increases at 40 and 100 ppb were significantly greater than at 0 ppb (P less than 0.05). The increase in Vf with exposure to 100 ppb and the decline at 1000 ppb parallel the results observed for chromosome damage in spleen lymphocytes from the same animals (Au et al., Mutation Res., 260 (1991) 219-224). These results indicate that sub-chronic exposure to benzene at levels below the current Occupational Safety and Health Administration Permitted Exposure Limit may induce gene mutations in lymphocytes in mice.

Male and female CD-1 mice were exposed to near ambient air concentrations of benzene by inhalation for 22 h per day, 7 days per week for 6 weeks. The concentrations were 0, 40, 100 and 1000 ppb. Significant increases in chromosome aberrations in spleen lymphocytes were observed in exposed compared with control mice except in the high-dose group (p less than 0.05 for female mice in 2 experiments and for male mice in 1 experiment; p less than 0.15 for male mice in the second experiment). A lack of increase in aberrations among mice of the high-dose group may be due to an induction of detoxifying enzymes as observed by us in a previous study (Au et al., 1988b). We also found that the female mice were more sensitive to the clastogenic activity of benzene than male mice under our experimental conditions. Our study serves to emphasize the need to conduct subchronic, low-dose in vivo genotoxicity studies using exposure conditions similar to those of humans, for evaluation of potential hazards. Our data suggest that the current occupational exposure concentrations for benzene (less than 1000 ppb) may still be hazardous to humans.

Praziquantel (PQ) is a commonly used drug to treat patients with schistosomiasis. Previous studies using cells in vitro have shown that PQ can enhance the mutagenic activities of known mutagens. We have conducted a cytogenetic - urine metabolite study to determine the in vivo clastogenic and co-clastogenic potential of PQ with a ubiquitous environmental contaminant, benzene (BZ). 16 groups of adult male ICR mice (5 animals per group) were used. They were negative control, solvent controls (cremophore E1 3%, olive oil and combined), positive control (BZ 440 mg/kg b.w.) and 11 exposed groups. To test for clastogenicity of PQ, mice were treated orally with 100, 400, 800 and 1200 mg/kg b.w. PQ and sacrificed 30 h later for determination of micronuclei (MN) frequency in bone-marrow polychromatic erythrocytes (PCE). None of these PQ does induced an increase of MN frequency. On the other hand, BZ induced, as expected, a high frequency of MN (46.4 +/- 6.34/1000 PCE). The enhancement effect of PQ was tested in 7 groups of mice using 3 different protocols. Mice were treated with 440 mg/kg b.w. BZ and 1 h later with 0, 100, 200, 400, 800 and 1200 mg/kg b.w. PZ. In another group, 800 mg/kg PQ was administered at 3 h after BZ exposure. In the last group, PQ (800 mg/kg) was administered at 1 h prior to BZ exposure. Results from the first combined exposure group showed a significant PQ dose-dependent increase in the frequency of MN in PCE (p less than 0.05). The increase with the two high doses of praziquantel is significantly higher (p less than 0.05) than the MN frequencies in the benzene control and the expected value based on the additive effects of the two agents. Studies with other combined treatment groups showed that the induction of MN was highest when PQ was administered at 1 h before BZ exposure. Moreover, the presence of BZ metabolites (muconic acid, phenol, catechol and hydroquinone) in urine was studied in 6 of the combined treatment groups. This metabolite study revealed that PQ enhanced the metabolism of BZ towards the pathway to form muconaldehyde which is converted to muconic acid in urine. In conclusion, our study showed that PQ is not a clastogen but can enhance the clastogenic activity of BZ in vivo by shifting the metabolic pathways of BZ towards formation of muconaldehyde which may be responsible for the enhancement effect.

The urine of a cigarette smoker who excretes exceptionally mutagenic urine was analyzed for several factors affecting mutagenicity. S. typhimurium strain TA98 was always more sensitive to XAD-2 urine concentrates than TA100. With TA98, as high as 85 revertants per ml of urine were produced. It was observed that incubation with beta-glucuronidase was not required for expression of mutagenicity but that a complete S9 mix was needed to convert the material in the concentrate to the ultimate mutagenic species. TLC and HPLC separation of the XAD-2 urine concentrate resulted in the identification of trace amounts of the bladder carcinogen, 2-aminonaphthalene (beta-naphthylamine) and a considerable amount of a possible metabolite of 2-aminonaphthalene, 2-amino-7-naphthol. The identity of the compounds was confirmed by mass spectral analysis, and 2-amino-7-naphthol was shown to be a mutagen for TA100 and TA98 when activated by rat-liver S9.

A study was conducted using a combined testing protocol (CTP), to determine whether short-term biological end-points, singly or in combination, are sufficiently sensitive to identify damage induced by exposure to ambient levels of industrial chemicals. A small-scale inhalation set-up which is both economical and easy to assemble was designed. Mice were exposed to 4 concentrations of a custom-blend mixture of benzene, chloroprene, epichlorohydrin and xylene in a ratio of 2:2:1:2, respectively. The concentrations for benzene, chloroprene and xylene were 0, 0.1, 1.0 and 10 ppm each. Concentrations for epichlorohydrin were half those for the other components. Groups of 22 males and 22 female mice were exposed to each concentration of the mixture for 3 and 6 weeks. Selected biological end-points including urine mutagenesis, bone marrow cell aberrations and micronuclei, spleen lymphocyte aberrations and liver enzyme induction were monitored. The spleen lymphocyte aberrations and liver enzyme induction were the most sensitive end-points. The lymphocytes showed a significant induction of chromosome aberrations from exposure for 3 weeks to all 3 concentrations of the mixtures. After 6 weeks of exposure, significant induction of aberrations was observed after exposure to low and medium concentrations but not to the high concentration. This lack of response at the high concentration after 6 weeks exposure, appeared to correlate with a significant induction of glutathione S-transferase in the liver. Since this enzyme is known to detoxify 3 of the 4 chemicals in our mixture, it may indicate a detoxification mechanism after enzyme induction. The present study indicates that the CTP is sufficiently sensitive to identify toxicological effects after exposure to ambient levels of a gas mixture.

19 aromatic amines were assayed for mutagenicity using Salmonella typhimurium strains TA98 and TA100 with and without the addition of S9 from Aroclor-1254-induced rat liver. These included: naphthalenes (1-amino-, 1-acetamido-, 2-amino-, 2-acetamido-, 1-amino-4-nitro- and 2-amino-1-nitro-), biphenyls (2-amino-, 2-acetamido-, 4-amino- and 4-acetamido-), fluorenes (2-amino- and 2-acetamido-), anthracenes (1-amino-, 1-acetamido-, 2-amino- and 2-acetamido-), 3-aminofluoranthene, 1-aminopyrene and 6-aminochrysene. None of the compounds were mutagenic when tested without S9. With S9, 15 of 19 were mutagenic for TA98 and 16 of the 19 were mutagenic for TA100. Overall, 2-aminoanthracene was the most potent mutagen. When compared to the parent amines, the respective acetamido derivatives were consistently less mutagenic.

The micronucleus test was performed in male ICR Swiss mice following modification of benzene metabolism by co-administration of aniline, pyridine or naphthalene, or by prior injection of alpha-naphthoflavone. HPLC profiles of urinary metabolites were compared to the effects of these compounds on clastogenicity. Pyridine inhibited both benzene clastogenicity and its metabolism. Aniline and naphthalene increased the clastogenicity and slightly altered the metabolism of benzene. alpha-Naphthoflavone inhibited benzene clastogenicity and metabolism only at high doses. Since 3-methylcholanthrene and phenobarbital both increase the metabolism of benzene but only 3-methylcholanthrene increases benzene clastogenicity, specific P450 isozymes may be responsible for different biological effects of benzene, and alterations in these effects might be caused by a shift from one isozyme to another.

The induction of chromosome aberrations in lymphocytes of mice after subchronic exposure to benzene was investigated. 4 groups of 5 Swiss (ICR) male mice were given orally a solution of benzene every day for 14 days except days 5 and 10. The daily doses were 0, 36.6, 73.2 and 146.4 mg/kg. Mice were sacrificed on day 15, lymphocytes were obtained by perfusion of the spleen and the cells were cultured in RPMI 1640 medium. After 48 h of culture, cells were harvested for cytogenetic analysis. A significant dose-dependent increase in the frequency of cells with chromatid aberrations were found (p less than 0.001). A significant increase in polyploid cells were also observed (p less than or equal to 0.05). This study represents the first report on the induction of chromosome aberrations and polyploid cells in lymphocytes of mice after subchronic exposure to benzene. Such dual activity of benzene suggests that benzene may be responsible for more human health problems than currently estimated.