Quantification of DNA and hemoglobin adducts of 3,4-epoxy-1,2-butanediol in rodents exposed to 3-butene-1,2-diol.

1,3-Butadiene (BD) is a confirmed rodent carcinogen and a suspect human carcinogen that forms mutagenic epoxide metabolites during biotransformation. Species differences in the roles of individual DNA reactive intermediates in BD mutagenicity and carcinogenicity are not completely understood. Evidence suggests that 1,2:3,4-diepoxybutane (DEB) is responsible for the mutagenic effect induced by exposures to low concentrations of BD in mice and that metabolites of 3-butene-1,2-diol (BD-diol) are involved in the mutagenicity at high exposures in both mice and rats. Two reactive metabolites, 3,4-epoxy-1,2-butanediol (EB-diol) and hydroxymethylvinyl ketone (HMVK), are formed during the biotransformation of BD-diol and could potentially be involved in BD-diol associated mutagenicity. To examine the role of EB-diol in BD-diol mutagenicity we have evaluated the dosimetry of N7-(2,3,4-trihydroxybutyl)guanine (THB-Gua) and N-(2,3,4-trihydroxybutyl)valine (THB-Val) in female B6C3F1 mice and female F344 rats exposed by inhalation to 0, 6, 18 and 36 p.p.m. BD-diol for 4 weeks (6 h/day x 5 days/week). Results showed higher levels of both THB-Gua and THB-Val in mice than in rats. An evaluation of THB-Gua adducts showed virtually no differences between liver and lung for either species, suggesting that EB-diol is stable and is freely circulated. The data also indicated that THB adduct formation began to plateau around 18 p.p.m. in both species. Most importantly, the shape of the dose-response curve for THB adduct formation mimicked the one observed for hypoxanthine-guanine phosphoribosyltransferase (Hprt) mutation frequency. This showed that THB adducts, which are not thought to be responsible for causing the mutations, are good quantitative indicators of mutagenicity in rodents exposed to BD-diol. Although the potential contribution of HMVK still needs to be evaluated, the data suggest that EB-diol is responsible, at least in part, for BD-diol associated mutagenicity in rodents.

Transplacental mutagenicity of N-ethyl-N-nitrosourea at the hprt locus in T-lymphocytes of exposed B6C3F1 mice.

Previous studies have compared age-related differences in total mutagenic burden in mice of differing age (preweanling, weanling, or young adult) after single intraperitoneal (i.p.) injections of ethylnitrosourea (ENU). The purpose of the present investigation was to determine the effects of time elapsed since treatment on the frequency of hprt mutant T-cells (Mf) from mice treated transplacentally with single acute vs. multiple split doses of ENU. To this end, pregnant C57BL/6 mice (n = 13-16/group), which had been bred to C3H males, were given i.p. injections of 40 mg ENU/kg bw in a single dose on day 18 of gestation, in a split dose of 6 mg ENU/kg bw on days 12 through 18 of gestation, or DMSO vehicle alone. Groups of pups were necropsied on days 10, 13, 15 (single dose only), 17, 20, 40, and 70 postpartum for T-cell isolations and hprt Mf measurements using the T-cell cloning assay. The time required to reach maximum Mfs in T-cells isolated from thymus of transplacentally treated animals was 2 weeks, the same time span as previously observed after ENU treatment of adult, weanling, and preweanling mice. Mfs in T-cells isolated from spleens of control animals averaged 2.1 +/- 0.3 (SE) x 10(-6). In spleens of mice treated transplacentally with ENU in a single dose, Mfs reached a maximum at 15 days postpartum [84.7 +/- 15.8 (SE) x 10(-6)] and decreased to lower but still elevated levels at 40 days postpartum. In spleens of mice treated transplacentally with ENU in a split dose, Mfs reached a maximum at 13 days postpartum [74.0 +/- 16.3 (SE) x 10(-6)] and decreased to background levels at 40 days postpartum. The areas under the curves describing the change in hprt Mfs over time for ENU-treated vs. control mice estimate the mutagenic potency for transplacental single- and split-dose exposures to be 1.9 and 0.8 x 10(3), respectively. Comparison of the mutagenic potency estimates for mice exposed to ENU in utero to 4-week-old mice given a similar dose of the same lot number of ENU indicates that the mouse is more susceptible to ENU-induced mutagenesis during fetal life.

Mutagenicity at the Hprt locus in T cells of female mice following inhalation exposures to low levels of 1,3-butadiene.

A study was conducted to test the hypothesis that repeated low level exposures to 1,3-butadiene (BD), approaching the OSHA occupational threshold for this chemical, produce a significant mutagenic response in mice. Female B6C3F1 mice (4-5 weeks of age) were exposed by inhalation for 2 weeks (6 h/day, 5 days/week) to 0 or 3 ppm BD, and then necropsied at 4 weeks after the cessation of exposures to measure the frequency of mutations (MF) at the Hprt locus using the T-lymphocyte clonal assay. At necropsy, T cells were isolated from spleen and cultured in the presence of mitogen, growth factors, and a selection agent. Cells were scored for growth on days 8-9 after plating to determine cloning efficiencies (CEs) and Hprt MFs. There was a marginal but significant reduction in the growth of splenic T cells from mice exposed to 3 ppm (n=27) compared with control mice (n=24) (P=0.004), suggesting the occurrence of BD-induced cytotoxicity at this low exposure concentration. In addition, the average Hprt MF in mice exposed to 3 ppm BD [1.54+/-0.82 (S.D.)x10(-6)] was significantly increased by 1.6-fold over the average control value of 0.96+/-0.51 (S.D.)x10(-6) (P=0.004). Comparisons of these data to earlier Hprt mutagenicity studies of mice exposed to high concentrations of BD (where significant mutagenic but not cytotoxic effects were observed) indicate that the ability to detect the cytotoxic and mutagenic responses of T cells to low levels of BD was enhanced by using a much larger sample size than usual for both the control and treatment groups. Additional analyses of the quantitative relationships between CE and MF demonstrated that CE had no significant effect upon MF values in sham-exposed control mice or mice exposed to low-level BD. Furthermore, the approaches for assessing the impact of CE and clonality on Hprt MFs in these control and BD-exposed mice were applied with the same rigor as in in vivo Hprt mutagenicity studies in human children. The overall study results support the conclusion that short-term low-level BD exposure is mutagenic in the mouse.

Using DNA and hemoglobin adducts to improve the risk assessment of butadiene.

The purpose of this paper is to review what we know about various biomarkers of butadiene in animal, human and in vitro studies, and to draw inferences from these data that impact on the accurate assessment of human risks for cancer. Studies comparing the DNA and hemoglobin adducts of butadiene with exposure, metabolism and genotoxicity have provided a great deal of insight that is applicable to biologically based risk assessment. First, the DNA and hemoglobin adduct data strongly support the conclusion that 3,4-epoxy-1,2-butanediol is the major electrophile available for binding to these macromolecules. Biomarker studies have also provided insight into the possibility of a sensitive population associated with the GSTT1 null genotype. While it is clear that lymphocytes from GSTT1 null individuals are more sensitive for the induction of sister chromatid exchanges (SCE) following in vitro exposure to 1,2,3,4-diepoxybutane, there was no such increase in SCE or other biomarkers of genotoxicity in workers exposed to 1-3 p.p.m. butadiene, regardless of GST genotype. The globin adduct data also demonstrate that there is roughly a tenfold range for interindividual differences in the metabolism of butadiene. This type of analysis represents an excellent means for providing scientific data for this critical determinant. Another useful application of hemoglobin adducts in risk assessment was demonstrated by regressing data for various endpoints for genotoxicity against that individual's biologically effective dose, thereby providing an independent mechanism for evaluation that excludes any possible confounding by inappropriate controls. Finally, biomarker studies have identified critical gaps in our knowledge that are needed for the accurate assessment of butadiene. Most notable of these is the lack of diepoxide-specific biomarkers in mice, rats and humans.

Zidovudine-didanosine coexposure potentiates DNA incorporation of zidovudine and mutagenesis in human cells.

Drug combinations that include nucleoside reverse transcriptase inhibitors (NRTIs) are remarkably effective in preventing maternal-viral transmission of HIV during pregnancy. However, there may be potential long-term risks for children exposed in utero. Examination of the genotoxic and mutagenic effects of two NRTIs, zidovudine [AZT (3'-azido-3'-deoxythymidine)] and didanosine [ddI (2',3'-dideoxyinosine)], in cultured human lymphoblastoid cells revealed multiplicative synergistic enhancement of AZT-DNA incorporation and mutant frequency induction in response to the combined drug exposure, as compared with single-drug exposures. Dose-related increases in DNA incorporation of AZT (as measured by a competitive RIA) and mutagenicity at the HPRT and TK loci (as assessed by cell-cloning assays) were observed in cells exposed in culture to AZT, or equimolar combinations of AZT + ddI, at exposure concentrations ranging from 3 to 30 times the maximum plasma levels found in humans. Because mutagenesis is strongly associated with tumor induction in experimental models, children exposed transplacentally to combinations of NRTIs may be at risk for cancer development later in life.

Mutagenicity and loss of heterozygosity at the APRT locus in human lymphoblastoid cells exposed to 3'-azido-3'-deoxythymidine.

Previous experiments in our research group showed that 3'-azido-3'-deoxythymidine (AZT) caused increased mutant frequencies (Mfs) at the X-linked hypoxanthine-guanine phosphoribosyltransferase (HPRT) and the autosomal thymidine kinase (TK) genes in human lymphoblastoid cells and that there was a significant positive correlation between AZT incorporation into cellular DNA and AZT-induced TK Mfs. In the current study, the mutagenicity of AZT was further evaluated at the autosomal adenine phosphoribosyltransferase (APRT) gene. AZH1 cells, a human lymphoblastoid cell line heterozygous at the APRT locus, were exposed to 300 microM AZT for 0, 1, 3 or 6 days or to 0, 33, 100, 300 or 900 microM AZT for 3 days (n = 5 flasks/group). A cell cloning assay was used to quantitate APRT Mfs. AZT-induced APRT Mf increased with extended duration and with incremental concentrations of AZT exposure. There was a positive correlation (P = 0.022, coefficient = 0.93) between AZT incorporation into DNA and AZT-induced APRT Mfs. RFLP analyses indicated that AZT exclusively induced loss of heterozygosity in APRT mutants. These results, which are consistent with findings on the mutagenicity of AZT at the HPRT and TK genes, indicate the need for further investigations on the potential long-term side effects of AZT on humans, especially those who receive AZT for a prophylactic reason.

Biomarkers of exposure and effect as indicators of potential carcinogenic risk arising from in vivo metabolism of ethylene to ethylene oxide.

The purposes of the present study were: (i) to investigate the potential use of several biomarkers as quantitative indicators of the in vivo conversion of ethylene (ET) to ethylene oxide (EO); (ii) to produce molecular dosimetry data that might improve assessment of human risk from exogenous ET exposures. Groups (n = 7/group) of male F344 rats and B6C3F1 mice were exposed by inhalation to 0 and 3000 p. p.m. ET for 1, 2 or 4 weeks (6 h/day, 5 days/week) or to 0, 40, 1000 and 3000 p.p.m. ET for 4 weeks. N:-(2-hydroxyethyl)valine (HEV), N:7-(2-hydroxyethyl) guanine (N7-HEG) and HPRT: mutant frequencies were assessed as potential biomarkers for determining the molecular dose of EO resulting from exogenous ET exposures of rats and mice, compared with background biomarker values. N7-HEG was quantified by gas chromatography coupled with high resolution mass spectrometry (GC-HRMS), HEV was determined by Edman degradation and GC-HRMS and HPRT: mutant frequencies were measured by the T cell cloning assay. N7-HEG accumulated in DNA with repeated exposure of rodents to 3000 p.p.m. ET, reaching steady-state concentrations around 1 week of exposure in most tissues evaluated (brain, liver, lung and spleen). The dose-response curves for N7-HEG and HEV were supralinear in exposed rats and mice, indicating that metabolic activation of ET was saturated at exposures >/=1000 p.p.m. ET. Exposures of mice and rats to 200 p.p.m. EO for 4 weeks (as positive treatment controls) led to significant increases in HPRT: mutant frequencies over background in splenic T cells from exposed rats and mice, however, no significant mutagenic response was observed in the HPRT: gene of ET-exposed animals. Comparisons between the biomarker data for both unexposed and ET-exposed animals, the dose-response curves for the same biomarkers in EO-exposed rats and mice and the results of the rodent carcinogenicity studies of ET and EO suggest that too little EO arises from exogenous ET exposure to produce a significant mutagenic response or a carcinogenic response under standard bioassay conditions.

1,3-butadiene: cancer, mutations, and adducts. Part III: In vivo mutation of the endogenous hprt genes of mice and rats by 1,3-butadiene and its metabolites.

1,3-Butadiene (BD), an important chemical used mainly in the production of synthetic rubber, is a potent carcinogen in mice, a weak carcinogen in rats, and a suspected carcinogen in humans. To provide a better understanding of the mutagenic mechanisms involved in interspecies differences in BD-induced carcinogenesis, studies were conducted in rodents to test two hypotheses: (a) the mutagenic potency of BD at the hypoxanthine-guanine phosphoribosyltransferase (hprt) locus of T lymphocytes (T cells) can be used to quantify interspecies differences in BD-induced carcinogenicity in exposed rodents and (b) comparison of the mutagenic potency and specificity of BD and racemic mixtures of two epoxy metabolites, 1,2-epoxy-3-butene (BDO) and 1,2,3,4-diepoxybutane (BDO2), at the hprt locus of T cells can be used to define the relative contribution of each intermediate to observed BD mutagenicity in each species. The first hypothesis was investigated by determining the effects of exposure duration and elapsed time after exposures on hprt mutant frequencies (MFs) in T cells from thymus and spleen of female B6C3F1 mice and F344 rats (4 to 5 weeks old). In this study, rodents were exposed by inhalation to 0 or 1,250 parts per million (ppm) BD for up to 2 weeks, or to 0 or 625 ppm BD for up to 4 weeks (with all exposures 6 hours/day, 5 days/week). The second hypothesis was examined by defining the effects of exposure concentration and elapsed time after exposures on the hprt MFs in splenic T cells from mice and rats exposed by inhalation to BD (0, 20, 62.5, or 625 ppm), BDO (0, 2.5, or 25 ppm), or BDO2 (0, 2, or 4 ppm) for 4 weeks (all exposures 6 hours/day, 5 days/week). The hprt MFs were measured weekly or biweekly using the T cell cloning assay for up to 10 weeks after the last exposure. The mutagenic potency of BD (represented by the difference in the areas under the mutant T cell "manifestation" curves [or the "change in MFs over time"] of exposed versus control animals) was significantly greater in mice (4.4-fold) than in rats following 2 weeks of exposure to 1,250 ppm BD. Mutagenic potency in mice was 8.5-fold greater than that in rats following 4 weeks of exposure to 625 ppm BD. These hprt MF data provide the first evidence that BD is mutagenic in the rat, albeit the mutagenic response was significantly less than that observed in similarly exposed mice. In addition, the MF data from the two exposure-duration studies indicate that both exposure concentration and exposure duration are important in determining the magnitude of the mutagenic response to BD. The relative contribution of BDO versus BDO2 to overall BD mutagenicity was evaluated by exposing mice and rats to carefully chosen concentrations of BD and racemic mixtures of BDO and BDO2 (that is, 62.5, 2.5, and 4.0 ppm, respectively) and comparing the mutagenic potency of each compound when comparable blood levels of metabolites were achieved. The resulting MF data indicate that (+/-)-BDO2 is a major contributor to the mutagenicity of BD in mice at lower BD exposure levels (< or = 62.5 ppm), whereas other metabolites and stereochemical configurations are responsible for mutations in BD-exposed rats and for the incremental mutagenic effects at higher exposure levels in mice. Molecular analysis of hprt cDNA from expanded T cell clones from control and BD-exposed mice demonstrated an increased frequency of large deletions in exposed animals (p = 0.016), presumably associated with in situ formation of (+/-)-BDO2, meso-BDO2, or both. Results of these mutagenicity experiments, along with data from collaborative studies of DNA adducts from the same animals, should provide a better understanding of the interspecies variation in carcinogenic response to BD and improve the extrapolation of rodent data to the estimation of cancer risk in exposed persons.

Relationships between DNA incorporation, mutant frequency, and loss of heterozygosity at the TK locus in human lymphoblastoid cells exposed to 3'-azido-3'-deoxythymidine.

3'-Azido-3'-deoxythymidine (AZT), a thymidine analogue widely used in the treatment of AIDS patients and for prevention of the onset of AIDS in HIV-seropositive individuals, causes tumors in mice exposed as adults or in utero. The purpose of this study was to investigate the potential mechanisms of AZT mutagenicity and carcinogenicity by quantifying the incorporation of AZT into cellular DNA, measuring AZT-induced thymidine kinase (TK) mutant frequencies (Mfs), and determining the percentage of loss of heterozygosity (LOH) in spontaneous or AZT-induced TK mutants in the human lymphoblastoid cell line, TK6. Cells were exposed to 300 microM AZT for 0, 1, 3, or 6 days, or to 0, 33, 100, 300, or 900 microM AZT for 3 days (n = 5 flasks/group). The effects of exposure concentration on incorporation of AZT into cellular DNA were evaluated by an AZT radioimmunoassay, and the effects of duration and concentration of AZT exposure on the TK Mfs were assessed by a cell-cloning assay. AZT was incorporated into DNA in a dose-related manner at concentrations up to 300 microM, above which no further increase was observed. TK Mf increased with the extended duration and with incremental concentrations of AZT exposure. There was a positive correlation (P = 0.036, coefficient = 0.903) between AZT-DNA incorporation and AZT-induced TK Mfs, suggesting that AZT incorporation into cellular DNA has a direct role in the genotoxicity of AZT. Southern blot analyses indicated that 84% (6.2 x 10(-6)/7.4 x 10(-6)) of AZT-induced mutants were attributable to LOH, consistent with the known mechanism of AZT as a DNA chain terminator. Considering the importance of LOH in human carcinogenesis, AZT-induced LOH warrants further study.

Comparison of the mutations at Hprt exon 3 of T-lymphocytes from B6C3F1 mice and F344 rats exposed by inhalation to 1,3-butadiene or the racemic mixture of 1,2:3,4-diepoxybutane.

Experiments were conducted to define the spectra of mutations occurring in Hprt exon 3 of T-cells isolated from spleens of female B6C3F1 mice and F344 rats exposed by inhalation to 1,3-butadiene (BD) or its reactive metabolite, (+/-)-diepoxybutane (DEB). Hprt mutant frequencies (Mfs) in BD-exposed (1250 ppm for 2 weeks or 625 ppm for 4 weeks; 6 h/day, 5 days/week) and DEB-exposed (2 or 4 ppm for 4 weeks or 5 ppm for 6 weeks; 6 h/day, 5 days/week) mice and rats were significantly increased over concurrent control values. Mutant T-cell colonies from control and treated animals were screened for mutations in Hprt exon 3 using PCR amplification of genomic DNA and denaturing gradient gel electrophoresis, followed by sequence analysis. Exon 3 mutations were found at the following frequencies: 20/394 (5%) in control mice, 56/712 (8%) in BD-exposed mice, 59/1178 (5%) in BD-exposed rats, 66/642 (10%) in DEB-exposed mice, and 51/732 (7%) in DEB-exposed rats. Mutations in exposed animals included base substitutions, small deletions (1 to 74 bp), and small insertions (1 to 8 bp), with base substitutions predominating. Among the types of base substitutions observed in mice, the proportions of G.C-->A.T transitions (p=0.035, Fisher's Exact Test) and G.C-->C.G transversions (p=0.05) were significantly different in control vs. BD-exposed animals. Given the small number of exon 3 mutants analyzed, there was a high degree of overlap in the mutational spectra between BD-exposed mice and rats, between BD- and DEB-exposed mice, and between BD- and DEB-exposed rats in terms of the sites with base substitutions, the mutations found at those mutated sites, the relative occurrence of the most frequently observed base substitutions, and the occurrence of a consistent strand bias for the most frequently observed base substitutions. The spectra data suggest that adduction of both G.C and A.T bps is important in the induction of in vivo mutations by BD metabolites in exposed mice and rats.

Genotoxicity of 3'-azido-3'-deoxythymidine in the human lymphoblastoid cell line, TK6: relationships between DNA incorporation, mutant frequency, and spectrum of deletion mutations in HPRT.

Perinatal treatment with 3'-azido-3'-deoxythymidine (AZT) has been found to reduce the rate of maternal-infant transmission of HIV; however, AZT is genotoxic in mammalian cells in vitro and induces tumors in the offspring of mice treated in utero. The purpose of the present study was to investigate the relationships between incorporation of AZT into DNA, and the frequency and spectrum of mutations at the HPRT locus of the human lymphoblastoid cell line, TK6, following in vitro exposures to AZT. Cells were cultured in medium containing 0 or 300 microM AZT for 1, 3, or 6 day(s) (n = 5/group). The effects of exposure duration on incorporation of AZT into DNA and HPRT mutant frequency were determined using an AZT radioimmunoassay and a cell cloning assay, respectively. AZT accumulated in DNA in a supralinear manner, approaching a plateau at 6 days of treatment (101.9 +/- 14.7 molecules AZT/10(6) nucleotides). After 3 days of AZT exposure, HPRT mutant frequency was significantly increased (1.8-fold, p = 0.016) compared to background (mutant frequency = 3.78 x 10(-6)). Multiplex PCR amplification of genomic DNA was used to determine the frequency of exon deletions in HPRT mutant clones from untreated cells versus AZT-treated cells. Molecular analyses of AZT-induced mutations revealed a significant difference in the frequency of total gene deletions (44/120 vs. 18/114 in controls, p = 0.004 by the Mann-Whitney U-statistic). In fact, the Chi-square test of homogeneity demonstrate that the differences between the control and AZT-treatment groups is attributed mainly to this increase in total gene deletion mutations (p = 0.00001). These data indicate that the primary mechanism of AZT mutagenicity in human TK6 cells is through the production of large deletions which occur as a result of AZT incorporation into DNA and subsequent chain termination. The data imply that perinatal chemoprophylaxis with AZT may put children of HIV-infected women at potential risk for genetic damage.

Tissue-specific mutant frequencies and mutational spectra in cyclophosphamide-treated lacI transgenic mice.

The induction and nature of mutations in the lacI transgene were evaluated in multiple tissues after exposure of adult male B6C3F1 lacI transgenic mice to cyclophosphamide (CP). Mice were given a single i.p. injection of 25 mg CP/kg, 100 mg CP/kg, or vehicle (PBS) and then necropsied 6 weeks after treatment to allow DNA extraction and lacI mutant recovery. Tissues evaluated included target tissues for tumorigenesis (lung, urinary bladder) and sites not susceptible to tumor formation in B6C3F1 mice (kidney, bone marrow, splenic T-lymphocytes). After exposure to the high dose of CP, a significant increase in the mutant frequency (Mf) was detected in the lungs and urinary bladders, compared to the respective tissues from vehicle-treated controls. In contrast, the Mfs in kidney, bone marrow, and splenic T cells from CP-treated mice were not significantly different from controls. The spectra of mutations in lacI from lung and urinary bladder were significantly changed after high-dose CP treatment, with a significant increase in the frequency of A. T --> T. A transversions found in both tissues and a significantly elevated frequency of deletions in the lungs. Conversely, in vehicle-treated mice, the two predominant classes of lacI mutations recovered in lung and urinary bladder were G. C --> A. T transitions at CpG sites and G. C --> T. A transversions. These CP exposures were also genotoxic as measured by the significant induction of micronuclei in peripheral blood 48 hr after exposure. These data indicate that under these study conditions, CP-induced mutations are detectable in the lacI transgene in the target tissues, but not in nontarget tissues for CP-induced cancer. With the lacI assay it is possible to study mutagenicity in a variety of critical tissues to provide mechanistic information related to genotoxicity and carcinogenicity in vivo.

Detection of cyclophosphamide-induced mutations at the Hprt but not the lacI locus in splenic lymphocytes of exposed mice.

The relative sensitivities and specificities of the endogenous Hprt gene and the lacI transgene as mutational targets were evaluated in splenic lymphocytes from male standard B6C3F1 mice (only Hprt assayed) and from lacI transgenic B6C3F1 mice treated at 6-7 weeks- of-age with the indirect-acting agent, cyclophosphamide (CP). To define the effects of the time elapsed since CP treatment on Hprt mutant frequencies (Mfs), nontransgenic mice were given single i.p. injections of 25 mg CP/kg or vehicle (PBS) alone and then necropsied 2, 4, 6, 8, or 10 weeks after treatment. Peak Mfs were found at 6 weeks postexposure, with mean Mf values ranging from 2.27 to 3.27 x 10(-5) using two different lots of CP in standard packaging (compared with mean control Mf values of 0.14 to 0.26 x 10(-5) in various experiments). To determine the dose response for Hprt Mfs, nontransgenic mice were given single doses of 0, 12.5, 25, 50, or 100 mg CP/kg and necropsied 4 weeks postexposure. These treatments produced a supralinear dose response curve for CP-induced Hprt Mfs. Based on these experiments, CP mutagenicities at Hprt and lacI were compared in transgenic mice treated with 0, 25, or 100 mg CP/kg (using another lot of CP in ISOPAC((R)) bottles; Sigma) and necropsied 6 weeks later. There was a significant increase in Hprt Mfs in treated transgenic mice (100 mg CP/kg: 0.75 +/- 0.09 x 10(-5); 25 mg CP/kg: 0.39 +/- 0.05 x 10(-5)) versus controls (0.10 +/- 0.01 x 10(-5)); however, the Mfs in lacI of lymphocytes from the same CP-treated animals were not significantly different from controls (100 mg CP/kg: 9.4 +/- 1.1 x 10(-5); 25 mg CP/kg: 6.7 +/- 0. 8 x 10(-5); control: 7.7 +/- 0.7 x 10(-5)). Hprt mutational spectra data in CP-treated transgenic and nontransgenic mice were different from those of control mice, whereas the spectra of mutations in lacI of lymphocytes from Big Blue((R)) transgenic mice were not significantly changed after CP treatment. These data indicate that, under these treatment conditions, CP-induced mutations in splenic lymphocytes were detectable in the Hprt gene but not the lacI transgene of this nontarget tissue for CP-induced cancer.

Molecular dosimetry of endogenous and ethylene oxide-induced N7-(2-hydroxyethyl) guanine formation in tissues of rodents.

The formation of N7-(2-hydroxyethyl)guanine (7-HEG) in DNA was investigated previously in target and non-target tissues of F-344 rats and B6C3F1 mice exposed to >/=ISOdia>/=10 p.p.m. concentrations of ethylene oxide (EO) using fluorescence-linked high-performance liquid chromatography [V.E. Walker et al. (1992) Cancer Res., 52, 4238-4334]. In order to study the dose-responses for 7-HEG at lower exposures, a highly sensitive and specific gas chromatography coupled with high-resolution mass spectrometry (GC-HRMS) assay was developed. DNA was extracted from liver, brain, lung and spleen of B6C3F1 mice and F-344 rats exposed to 0, 3, 10, 33 or 100 p.p.m. EO for 4 weeks (6 h/day, 5 days/week). Analysis of DNA from control rodents showed that endogenous 7-HEG varied from 0.2 +/- 0.1 to 0.3 +/- 0.2 pmol/micromol guanine in tissues of rats and mice. 7-HEG exhibited tissue- and species-specific dose-response relationships in EO-exposed animals. Linear dose-response relationships were evident in mouse liver, brain and spleen at exposures between 3 and 100 p.p.m. Mouse lung exhibited a slightly sublinear response between 33 and 100 p.p.m. EO. The relationships were linear in liver and spleen of rats between 3 and 100 p.p.m. EO, but were slightly sublinear in brain and lung between 33 and 100 p.p.m. EO. The number of 7-HEG adducts present in rats exposed to 3 p.p.m. EO was 5.3-12.5 times higher than endogenous 7-HEG in unexposed controls. In contrast, mice exposed to 3 p.p.m. EO only had 1.3- to 2.5-fold greater numbers of 7-HEG adducts. The factors driving the exposure-response relationships are also likely to affect carcinogenic and mutagenic responses of rodents to EO. Likewise, a better understanding of the relationships between 7-HEG derived from low exposures to EO and endogenously formed 7-HEG may be important for the accurate extrapolation of risk to humans.

Mutagenicity of 1,3-butadiene at the Hprt locus of T-lymphocytes following inhalation exposures of female mice and rats.

The species specific response to 1,3-butadiene (BD), an important industrial chemical, was investigated by determining the influence of exposure duration and exposure concentration on the mutagenicity of BD in mice and rats and by defining the spectra of mutations in the Hprt gene T-cell mutants from control and BD-exposed mice. Female B6C3F1 mice and F344 rats (4-5 weeks old) were exposed by inhalation to 0, 20, 62.5, or 625 ppm of BD for up to 4 weeks (6 h/day, 5 days/week). Groups of control and exposed animals (n=4-12/group) were necropsied at multiple time points after exposure and the T-cell cloning assay was used to measure Hprt mutant frequencies in lymphocytes isolated from spleen. Mutant clones collected from control and BD-exposed mice were propagated and analyzed by RT-PCR to produce Hprt cDNA for sequencing. In animals necropsied 4 weeks after 2 or 4 weeks of BD exposure (0 or 625 ppm), the rate of accumulation of mutations was greater in mice than in rats. Supra-linear dose-response curves were observed in BD-exposed mice, indicating a higher efficiency of mutant induction at lower concentrations of BD. The mutagenic potency estimates (represented by the differences in the areas under the mutant T-cell 'manifestation' curves of treated vs. control animals) in mice were 11 and 61 following 4 weeks of exposures to 62.5 and 625 ppm of BD, respectively, while mutant frequencies (Mfs) in rats were significantly increased only at 625 ppm BD (mutagenic potency of 7). Molecular analysis of Hprt cDNA from expanded T-cell clones from control and BD-exposed mice demonstrated an increased frequency of mutants in exposed animals that likely contain large deletions in the Hprt gene (P=0.016). These data indicate that both exposure duration and exposure concentration are important in determining the magnitude of mutagenic response to BD, and that mutagenic and carcinogenic properties of BD in mice may be related more to the ability of its metabolites to cause chromosomal deletions than to produce point mutations.

Mutagenicity of the racemic mixtures of butadiene monoepoxide and butadiene diepoxide at the Hprt locus of T-lymphocytes following inhalation exposures of female mice and rats.

The purpose of this study was to determine if Hprt mutant frequency (Mf) data from rodents exposed directly to individual epoxy metabolites of 1,3-butadiene (BD) can be used to identify the relative significance of each intermediate in the mutagenicity of BD in mice vs. rats. To this end, the relative contributions of the racemic mixtures of BD monoepoxide (BDO) and BD diepoxide (BDO(2)) to BD-induced mutagenicity was investigated by exposing mice and rats to selected concentrations of BDO and BDO(2) (i.e., 2.5 and 4.0 ppm, respectively) and comparing the mutagenic potency of each intermediate to that of BD (at 62.5 ppm) when comparable blood levels of metabolites are achieved (in the mouse). Female B6C3F1 mice and F344 rats (4-5 weeks old) were exposed to rac-BDO (0, 2.5, or 25 ppm) or (+/-)-BDO(2) (0, 2, 4 ppm) by inhalation for 4 weeks (6 h/day, 5 days/week), and then groups of control and exposed animals (n=3-12/group) were necropsied at multiple time points post-exposure for measuring Hprt Mfs in splenic lymphocytes (via the T-cell cloning assay) and estimating mutagenic potencies (represented by the difference in the areas under the mutant T-cell 'manifestation' curves of treated vs. control animals). The resulting Mf data, along with the extant metabolism data, suggest that at lower BD exposures (

Molecular dosimetry of N-7 guanine adduct formation in mice and rats exposed to 1,3-butadiene.

1,3-Butadiene (BD) is a high-volume chemical used in the production of rubber and plastic. BD is a potent carcinogen in mice and a much weaker carcinogen in rats, and has been classified as a probable human carcinogen. Upon metabolic activation in vivo, it forms DNA-reactive metabolites, 1,2-epoxy-3-butene (EB), 1,2:3, 4-diepoxybutane (DEB), and 3,4-epoxy-1,2-butanediol (EBD). The molecular dosimetry of N-7 guanine adduct formation by these metabolites of BD in liver, lung, and kidney of B6C3F1 mice and F344 rats exposed to 0, 20, 62.5, or 625 ppm BD was studied. The adducts, racemic and meso forms of N-7-(2,3,4-trihydroxybut-1-yl)guanine (THB-Gua), N-7-(2-hydroxy-3-buten-1-yl)guanine (EB-Gua I), and N-7-(1-hydroxy-3-buten-2-yl)guanine (EB-Gua II), were isolated from DNA by neutral thermal hydrolysis, desalted on solid-phase extraction cartridges, and quantitated by LC/ESI(+)/MS/MS. The number of adducts per 10(6) normal guanine bases for a given adduct was higher in mice than rats exposed to 625 ppm BD, but generally similar at lower levels of exposure. The THB-Gua adducts were the most abundant (6-27 times higher than EB-Gua) and exhibited a nonlinear exposure-response relationship. In rats, the exposure-response curves for the formation of THB-Gua adducts reached a plateau after 62.5 ppm, suggesting saturation of metabolic activation. The number of THB-Gua adducts continued to increase in mice between 62.5 and 625 ppm BD. In contrast, the less common EB-Gua adducts had a linear exposure-response relationship in both species. Combining the information from this study with previous data on BD metabolism, we were able to estimate the number of THB-Gua that resulted from DEB and EBD, and conclude that most of the THB-Gua is formed from EBD. We hypothesize that most of the EBD arises from the immediate conversion of DEB to EBD within the endoplasmic reticulum. This study highlights the need for measurements of the levels of EBD in tissues of rats and mice and for the development of a unique biomarker for DEB that is available for binding to DNA.

Effect of coupling on volume-regulatory response of ciliary epithelial cells suggests mechanism for secretion.

The ciliary epithelium of the eye secretes the aqueous humor. It is a double epithelium arranged so that the apical surfaces of the nonpigmented ciliary epithelial (NPCE) and pigmented ciliary epithelial (PCE) cells face each other and the basolateral membranes face the inside of the eye and the blood, respectively. We have investigated the volume responses of both single cells and coupled pairs from this tissue to osmotic challenge. Both NPCE and PCE cells undergo regulatory volume increase (RVI) and decrease (RVD) when exposed to hyper- and hyposmotic solution, respectively. In hyposmotic solution single cells swell and return to their original volumes within approximately 3 min. In nonpigmented cells RVD could be inhibited by blockers of volume-activated Cl- channels [tamoxifen (100%) > quinidine (87%) > DIDS (84%) > 5-nitro-2-(3-phenylpropylamino)benzoic acid (80%) > SITS (58%)] and K+ channels [Ba2+ (31%)]. However, in PCE cells these inhibitors and additionally tetraethylammonium and Gd3+ were without effect. Only bumetanide, an inhibitor of Na+-K+-2Cl- cotransport, was found to have any effect on RVD in PCE cells. NPCE-PCE cell coupled pairs also underwent RVD, but with altered kinetics. The onset of RVD of the PCE cell in a pair occurred approximately 80 s before that of the NPCE cell, and the peak swell was reduced. This is consistent with fluid movement from the PCE to the NPCE cell. The effect of the volume-activated Cl- channel inhibitor tamoxifen was to eliminate this difference in the times of onset of RVD in coupled cell pairs and to inhibit RVD in both the NPCE and PCE cells partially. On the basis of these observations we suggest that fluid is transferred from the PCE to the NPCE cell in coupled pairs during cell swelling and the subsequent RVD. Furthermore, we speculate that reciprocal RVI-RVD could underlie aqueous humor secretion.

Persistence of N7-(2,3,4-trihydroxybutyl)guanine adducts in the livers of mice and rats exposed to 1,3-butadiene.

Liquid chromatography (LC) in combination with tandem mass spectrometry (MS/MS) and stable isotope methodology was employed for the analysis of the N7-guanine (Gua) adducts derived from 1,2:3, 4-diepoxybutane (BDO2) a reactive metabolite of 1,3-butadiene (BD). Two diastereomeric forms of N7-(2,3,4-trihydroxybutyl)guanine (THBG) were identified in the livers of both mice and rats. One of the diastereomers [(+/-)-THBG] was formed by reaction of DNA with (+/-)-BDO2, and the other diastereomer (meso-THBG) was formed by reaction of DNA with meso-BDO2. There was significantly more (+/-)-THBG and meso-THBG in the liver DNA of the mice when compared with those of the rats during the 10 days of exposure to BD and the 6 days of postexposure that were monitored. There was a 2-fold excess of (+/-)-THBG over meso-THBG in the rat liver at all the time points. In the mouse liver after 10 days of exposure to BD, the (+/-)-THBG (3.9 adducts/10(6) normal bases) was also present in an almost 2-fold excess over meso-THBG (2.2 adducts/10(6) normal bases). However, 6-days after exposure to BD, (+/-)-THBG (1.2 adducts/10(6) normal bases) and meso-THBG (1.0 adduct/10(6) normal bases) were present in almost equal amounts in the mouse liver. Furthermore, there was an almost 5-fold excess of the two THBG diastereomers in the mouse liver DNA 6 days after exposure to BD when compared with rat liver DNA. The half-lives of (+/-)-THBG and meso-THBG appeared to be slightly longer in mouse liver (4.1 and 5.5 days, respectively) than in rat liver (3.6 and 4.0 days, respectively). The apparent persistence of these adducts in the mouse may contribute to the increased susceptibility of this species to BD-induced carcinogenesis. It is possible that (+/-)-THBG and meso-THBG could have also been derived from the reaction of DNA with the hydrolysis product of BDO2, 1,2-dihydroxy-3,4-epoxybutane (DHEB). Surprisingly, a vast majority of the studies in which the mutagenic and carcinogenic potential of BDO2 have been examined have only employed the commercially available (+/-)-BDO2. In light of the present findings, additional studies will be required to determine the potency of meso-BDO2 and the DHEB that is the precursor to meso-THBG as mutagens and carcinogens.

Relationships between exposure, cell loss and proliferation, and manifestation of Hprt mutant T cells following treatment of preweanling, weanling, and adult male mice with N-ethyl-N-nitrosourea.

Experiments were performed to characterize the age-related patterns of appearance and frequency of hypoxanthine-guanine phosphoribosyl transferase (Hprt) mutant T lymphocytes in thymus and spleen following exposure of preweanling (12-day-old), weanling (22-day-old), and young adult (8-week-old) male B6C3F1 mice to ethylnitrosourea (ENU). Mice were given single i.p. injections of 0 or 40 mg ENU/kg and then groups of animals were necropsied from 2 h to 116 days after treatment to examine the relationships between exposure, cell loss and proliferation, and the frequency of Hprt mutant T cells in thymus and spleen. Hprt mutant frequency (Mf) data for thymus of ENU-exposed (0, 11.7, 35, 58, or 72 mg/kg, or five weekly doses of 1.7 mg/kg i.p.) male C57BL/6 mice (12- or 62-week-old), obtained during an earlier study of spleen cells [I.M. Jones, K. Burkhart-Schultz, C.L. Strout, T.L. Crippen, Factors that affect the frequency of thioguanine-resistant lymphocytes in mice following exposure to ethylnitrosourea, Environ. Mutagen, 9 (1987) 317-329.], were compared to results in B6C3F1 mice. Isolated T cells were cultured in the presence of mitogen, growth factor, and 6-thioguanine to detect Hprt mutants. The time required to achieve maximum Mfs in thymus was uniformly found at 2 weeks after ENU treatment, while the times needed to reach peak values in spleen were proportional to animal age at treatment. These data indicate that age-related differences in the appearance of Hprt mutant cells in spleen are largely defined by the physiologically based, age-dependent trafficking of mutant cells from or through the thymus. Three modes of handling the resulting Hprt Mf data were evaluated: (i) comparing the Mfs at a single time point, (ii) comparing the maximum Mfs observed, and (iii) comparing the change in Mfs over time (or the mutant T cell 'manifestation' curves in treated vs. control mice) in each age group post-exposure. Measuring the Mfs in spleen at multiple time points after cessation of exposure and integrating the frequency of mutants as a function of time appeared to be the superior method for comparing mutagenic responses in different age groups. Some of the underlying assumptions of this approach, as well as its strengths and weaknesses, are discussed.