Inhibitory effect of benzene metabolites on nuclear DNA synthesis in bone marrow cells

Effects of endogenously produced and exogenously added benzene metabolites on the nuclear DNA synthetic activity were investigated using a culture system of mouse bone marrow cells. Effects of the metabolites were evaluated by a 30-min incorporation of [3H]thymidine into DNA following a 30-min interaction with the cells in McCoy's 5a medium with 10% fetal calf serum. Phenol and muconic acid did not inhibit nuclear DNA synthesis. However, catechol, 1,2,4-benzenetriol, hydroquinone, and p-benzoquinone were able to inhibit 52, 64, 79, and 98% of the nuclear DNA synthetic activity, respectively, at 24 microM. In a cell-free DNA synthetic system, catechol and hydroquinone did not inhibit the incorporation of [3H]thymidine triphosphate into DNA up to 24 microM but 1,2,4-benzenetriol and p-benzoquinone did. The effect of the latter two benzene metabolites was completely blocked in the presence of 1,4-dithiothreitol (1 mM) in the cell-free assay system. Furthermore, when DNA polymerase alpha, which requires a sulfhydryl (SH) group as an active site, was replaced by DNA polymerase I, which does not require an SH group for its catalytic activity, p-benzoquinone and 1,2,4-benzenetriol were unable to inhibit DNA synthesis. Thus, the data imply that p-benzoquinone and 1,2,4-benzenetriol inhibited DNA polymerase alpha, consequently resulting in inhibition of DNA synthesis in both cellular and cell-free DNA synthetic systems. The present study identifies catechol, hydroquinone, p-benzoquinone, and 1,2,4-benzenetriol as toxic benzene metabolites in bone marrow cells and also suggests that their inhibitory action on DNA synthesis is mediated by mechanism(s) other than that involving DNA damage as a primary cause.     

DNA damage in L5178YS cells following exposure to benzene metabolites

Because DNA modification may be a prerequisite for chemical carcinogenesis, the DNA-damaging potential of benzene and its metabolites was examined in order to identify the proximate DNA-damaging agent associated with benzene exposure. A DNA synthesis inhibition assay previously identified p-benzoquinone as the most potent overall cellular toxin and inhibitor of DNA synthesis, but failed to discriminate among the hydroxylated metabolites. Therefore, the ability of benzene and its metabolites to induce DNA strand breaks in the mouse lymphoma cell line, L5178YS, was examined in order to provide a more accurate indication of the DNA damage associated with benzene and its metabolites. Cells were exposed to benzene, hydroquinone, catechol, phenol, 1,2,4-benzenetriol, or p-benzoquinone over a 1000-fold concentration range (1.0 microM-1.0 mM). Concentrations of benzene, phenol, or catechol as high as 1.0 mM did not increase the percentage of single-stranded DNA observed. Concentrations of hydroquinone as high as 0.1 mM were also ineffective. In contrast, both p-benzoquinone and 1,2,4-benzenetriol produced DNA breaks in a dose-related fashion. Of the two, benzoquinone proved to be more potent with an ED50 of approximately equal to 2.5 microM compared with 55.0 microM for benzenetriol. The DNA damage induced by 6.0 microM benzoquinone was maximal within 3 min of exposure and yielded approximately 70% single-stranded DNA after alkaline denaturation. By contrast, the single-stranded DNA observed after benzenetriol exposure required 60 min of exposure to achieve the same extent of damage as that found with benzoquinone. These results suggest that the benzene metabolites, benzenetriol and benzoquinone, may cause DNA damage and that the mechanisms responsible for the damage associated with these two compounds may be different.     

In vitro effects of benzene metabolites on mouse bone marrow stromal cells

Benzene exposure can result in bone marrow myelotoxicity. We examined the effects of benzene metabolites on bone marrow stromal cells of the hemopoietic microenvironment. Male B6C3F1 mouse bone marrow adherent stromal cells were plated at 4 X 10(6) cells per 2 ml of DMEM medium in 35-mm tissue culture dishes. The growing stromal cell cultures were exposed to log 2 doses of five benzene metabolites: hydroquinone, benzoquinone, phenol, catechol, or benzenetriol for 7 days. The dose which caused a 50% decrease in colony formation (TD50) was 2.5 X 10(-6) M for hydroquinone, 17.8 X 10(-6) M for benzoquinone, 60 X 10(-6) M for benzenetriol, 125 X 10(-6) M for catechol, and 190 X 10(-6) M for phenol. We next examined the effect of benzene metabolites on the ability of stromal cells to influence granulocyte/monocyte colony growth (G/M-CFU-C) in a coculture system. Adherent stromal cells were plated and incubated for 14 days and then exposed to a benzene metabolite. After 3 days the medium and metabolite were removed and an agar:RPMI layer containing 10(6) fresh bone marrow cells was placed over the stromal layer. After incubation for 7 days the cultures were scored for G/M colony formation. Hydroquinone and benzoquinone were most toxic, while catechol and benzenetriol inhibited colony growth only at high doses. These results indicate that injured bone marrow stromal cells may be a significant factor in benzene-induced hemotoxicity.     

Evidence for strain-specific differences in benzene toxicity as a function of host target cell susceptibility

It has long been recognized that benzene exposure produces disparate toxic responses among different species or even among different strains within the same species. There is ample evidence that species- or strain-dependent differences in metabolic activity correlate with the disparate responses to benzene. However, bone marrow cells (the putative targets of benzene toxicity) may also exhibit species- or strain-dependent differences in susceptibility to the toxic effects of benzene. To investigate this hypothesis, two sets of companion experiments were performed. First, two strains of mice, Swiss Webster (SW) and C57B1/6J (C57), were exposed to 300 ppm benzene via inhalation and the effects of the exposures were determined on bone marrow cellularity and the development of bone marrow CFU-e (Colony Forming Unit-erythroid, an early red cell progenitor). Second, bone marrow cells from the same strains were exposed in vitro to five known benzene metabolites (1,4 benzoquinone, catechol, hydroquinone, muconic acid, and phenol) individually and in binary combinations. Benzene exposure, in vivo, reduced bone marrow cellularity and the development of CFU-e in both strains; however, reductions in both these endpoints were more severe in the SW strain. When bone marrow cells from the two strains were exposed in vitro to the five benzene metabolites individually, benzoquinone, hydroquinone, and catechol reduced the numbers of CFU-e in both strains in dose-dependent responses, phenol weakly reduced the numbers of the C57 CFU-e only and in a non-dose-dependent manner, and muconic acid was without effect on cells from either strain. Only benzoquinone and hydroquinone exhibited differential responses to CFU-e from the two strains and both of these metabolites were more toxic to SW cells than to C57 cells. Six of the ten possible binary mixtures of metabolites were differentially toxic to the CFU-e from the two strains and five of these mixtures were more toxic to SW cells than to C57 cells. Thus, SW mice were more susceptible to the toxic effects of inhaled benzene and their bone marrow cells were more severely affected by in vitro exposure to benzene metabolites. The binary combinations containing phenol produced little or no enhancement of the toxic effects of the non-phenol metabolites. The weak toxic response induced by phenol, whether delivered alone or in binary mixtures, suggests that little metabolism occurred during the 48 h of the in vitro exposures since benzoquinone and hydroquinone, which were clearly toxic when added to the CFU-e culture system, are formed by further metabolic oxidation of phenol. Thus, strain-dependent differential metabolism appeared to play a minimal role in the disparate toxicity observed in the in vitro studies, implying that the diverse responses were due to inherent differences in the susceptibilities of the CFU-e to the toxic action of the benzene metabolites.     

Relationship between the oxidation potential of benzene metabolites and their inhibitory effect on DNA synthesis in L5178YS cells

The effects of benzene and its metabolites on the rate of DNA synthesis were measured in the mouse lymphoma cell line, L5178YS. The direct toxicity of benzene could be distinguished from that of its metabolites since bioactivation of benzene in L5178YS cells was not observed. Cells were exposed to benzene, phenol, catechol, hydroquinone, p-benzoquinone, or 1,2,4-benzenetriol over the range of 1.0 X 10(-7) to 1.0 X 10(-2) M for 30 min, and the rate of DNA synthesis was measured at various times after chemical washout. Cell viability and protein synthesis were determined by trypan blue dye exclusion and [3H]leucine incorporation, respectively. Effects were designated as "DNA specific" when DNA synthesis was inhibited in the absence of discernible effects on cell membrane integrity and protein synthesis. Concentrations of benzene as high as 1 mM had no effect on DNA synthesis. Comparison of the effects at the maximum nontoxic dose for each compound showed that catechol and hydroquinone were the most effective, inhibiting DNA synthesis by 65%. Phenol, benzoquinone, and benzenetriol inhibited DNA synthesis by approximately 40%. Maximum inhibition was observed 60 min after metabolite washout in each case. Benzoquinone was the most potent inhibitor of DNA synthesis, followed by hydroquinone, benzenetriol, catechol, and phenol with ED50 values of 5 X 10(-6), 1 X 10(-5), 1.8 X 10(-4), 2.5 X 10(-4), and 8.0 X 10(-4), respectively. Cyclic voltammetric experiments were performed on the hydroxylated metabolites of benzene to assess the possible involvement of a redox-type mechanism in their inhibition of DNA synthesis. The ease of oxidation of these metabolites correlated with their ED50 values for inhibition of DNA synthesis (r = 0.997). This suggests that oxidation of phenol or one of its metabolites may be necessary for production of the species involved in inhibition of DNA synthesis.     

An interaction of benzene metabolites reproduces the myelotoxicity observed with benzene exposure

Benzene-induced myelotoxicity can be reproduced by the coadministration of two principal metabolites, phenol and hydroquinone. Coadministration of phenol (75 mg/kg) and hydroquinone (25-75 mg/kg) twice daily to B6C3F1 mice for 12 days resulted in a significant loss in bone marrow cellularity in a manner exhibiting a dose-response. One explanation for this potentiation is that phenol stimulates the peroxidase-dependent metabolism of hydroquinone. Addition of phenol to incubations containing horseradish peroxidase, H2O2, and hydroquinone resulted in a stimulation of both hydroquinone removal and benzoquinone formation. Stimulation occurred with phenol as low as 100 microM and with very low concentrations of horseradish peroxidase. When boiled rat liver protein was added to identical incubations containing [14C]hydroquinone, the level of radioactivity recovered as protein bound increased by 37% when phenol was added. Similar results were observed when [14C]hydroquinone was incubated in the presence of activated human leukocytes. Hydroquinone binding was increased by approximately 70% in the presence of phenol. Phenol-induced stimulation of hydroquinone metabolism and benzoquinone formation represents a likely explanation for the bone marrow suppression associated with benzene toxicity.     

Effects of co-exposure to extremely low frequency (ELF) magnetic fields and benzene or benzene metabolites determined in vitro by the alkaline comet assay

In the present study, we investigated in vitro the possible genotoxic and/or co-genotoxic activity of 50 Hz (power frequency) magnetic fields (MF) by using the alkaline single-cell microgel-electrophoresis (comet) assay. Sets of experiments were performed to evaluate the possible interaction between 50 Hz MF and the known leukemogen benzene. Three benzene hydroxylated metabolites were also evaluated: 1,2-benzenediol (1,2-BD, catechol), 1,4-benzenediol (1,4-BD, hydroquinone), and 1,2,4-benzenetriol (1,2,4-BT). MF (1 mT) were generated by a system consisting of a pair of parallel coils in a Helmholtz configuration. To evaluate the genotoxic potential of 50 Hz MF, Jurkat cell cultures were exposed to 1 mT MF or sham-exposed for 1h. To evaluate the co-genotoxic activity of MF, the xenobiotics (benzene, catechol, hydroquinone, and 1,2,4-benzenetriol) were added to Jurkat cells subcultures at the beginning of the exposure time. In cell cultures co-exposed to 1 mT (50 Hz) MF, benzene and catechol did not show any genotoxic activity. However, co-exposure of cell cultures to 1 mT MF and hydroquinone led to the appearance of a clear genotoxic effect. Moreover, co-exposure of cell cultures to 1 mT MF and 1,2,4-benzenetriol led to a marked increase in the genotoxicity of the ultimate metabolite of benzene. The possibility that 50 Hz (power frequency) MF might interfere with the genotoxic activity of xenobiotics has important implications, since human populations are likely to be exposed to a variety of genotoxic agents concomitantly with exposure to this type of physical agent.     

Benzene disposition in the rat after exposure by inhalation.

Little information is available on benzene disposition after exposure by inhalation despite the importance of this route in man. Benzene metabolites as a group have been measured in bone marrow, but quantitation of individual metabolites in this target tissue has not been reported. Male Fischer-344 rats were exposed to 500 ppm benzene in air and the uptake and elimination was followed in several tissues. Concentrations of free phenol, catechol, and hydroquinone in blood and bone marrow were also measured. Steady-state concentrations of benzene (11.5, 37.0, and 164.0 μg/g in blood, bone marrow, and fat, respectively) were achieved within 6 hr in all tissues studied. Benzene half-lives during the first 9 hr were similar in all tissues (0.8 hr). A plot of amount of benzene remaining to be excreted in the expired air was biphasic with $\text{t}\text{1}\text{2}$ values for the α and β phases of 0.7 and 13.1 hr, respectively. Phenol was the main metabolite in bone marrow at early times (peak concentration, 19.4 μg/g). Catechol and hydroquinone predominated later (peak concentrations, 13.0 and 70.4 μg/g, respectively). Concentrations of these two metabolites declined very slowly during the first 9 hr. These data indicate that free catechol and hydroquinone persist in bone marrow longer than benzene or free phenol.     

Cell-specific metabolism in mouse bone marrow stroma: studies of activation and detoxification of benzene metabolites.

Two of the major cell types in bone marrow stroma, macrophages and fibroblasts, have been shown to be important regulators of both myelopoiesis and lymphopoiesis. The enzymology relating to cell-specific metabolism of phenolic metabolites of benzene in isolated mouse bone marrow stromal cells was examined. Fibroblastoid stromal cells had elevated glutathione-S-transferase (4.5-fold) and DT-diaphorase (4-fold) activity relative to macrophages, whereas macrophages demonstrated increased UDP-glucuronosyltransferase (UDP-GT, 7.5-fold) and peroxidase activity relative to stromal fibroblasts. UDP-GT and glutathione-S-transferase activities in macrophages and fibroblasts, respectively, were significantly greater than those in unpurified white marrow. Aryl sulfotransferase activity could not be detected in either bone marrow-derived macrophages or fibroblasts, and there were no significant differences in GSH content between the two cell types. Because UDP-GT activity is high in macrophages, these data suggest that DT-diaphorase levels would be rate limiting in the detoxification of benzene-derived quinones in bone marrow macrophages. The peroxidase responsible for bioactivation of benzene-derived phenolic metabolites in bone marrow macrophages is unknown but has been suggested to be prostaglandin H synthase (PGS). Hydrogen peroxide, but not arachidonic acid, supported metabolism of hydroquinone to reactive species in bone marrow-derived macrophage lysates. These data do not support a major role for PGS in peroxidase-mediated bioactivation of hydroquinone in bone marrow-derived macrophages, although PGS mRNA could be detected in these cells. Similarly, hydrogen peroxide, but not arachidonic acid, supported metabolism of hydroquinone in a human bone marrow homogenate. Peroxidase-mediated interactions between phenolic metabolites of benzene occurred in bone marrow-derived macrophages. Bioactivation of hydroquinone to species that would bind to acid-insoluble cellular macromolecules was increased by phenol and was markedly stimulated by catechol. Bioactivation of catechol was also stimulated by phenol but was inhibited by hydroquinone. These data define the enzymology and the cell-specific metabolism of benzene metabolites in bone marrow stroma and demonstrate that interactions between phenolic metabolites may contribute to the toxicity of benzene in this critical bone marrow compartment.     

Modulation of the toxicity and macromolecular binding of benzene metabolites by NAD(P)H:Quinone oxidoreductase in transfected HL-60 cells.

Benzene is oxidized in the liver to produce a series of hydroxylated metabolites, including hydroquinone and 1,2,4-benzenetriol. These metabolites are activated to toxic and genotoxic species in the bone marrow via oxidation by myeloperoxidase (MPO). NAD(P)H:quinone oxidoreductase (NQO1) is an enzyme capable of reducing the oxidized quinone metabolites and thereby potentially reducing their toxicities. We introduced the NQO1 gene into the HL-60 cell line to create a high MPO-, high NQO1-expressing cell line, and tested its response in assays of benzene metabolite toxicity. NQO1 expression reduced a class of hydroquinone- and benzenetriol-induced DNA adducts by 79-86%. The cytotoxicity and apoptosis caused by hydroquinone were modestly reduced, while protein binding was unchanged and the rate of glutathione depletion increased. NQO1's activity in reducing a class of benzene metabolite-induced DNA adducts may be related to its known activities in maintaining membrane-bound endogenous antioxidants in reduced form. Alternatively, NQO1 activity may prevent the formation of adducts which result from polymerized products of the quinones. In either case, this protection by NQO1 may be an important mechanism in the observation that a lack of NQO1 activity affords an increased risk of benzene poisoning in exposed individuals [Rothman, N., et al. (1997) Cancer Res. 57, 2839-2842].     

Toxic effects of benzene and benzene metabolites on mononuclear phagocytes

Benzene is a potent bone marrow toxin in animals and man. Animal studies have shown that exposure to benzene can alter T lymphocyte functions and decrease the resistance of animals to Listeria monocytogenes and transplanted tumor cells. Mononuclear phagocytes participate in host resistance to Listeria and tumor cells. The purpose of the studies presented here was to determine the effects of benzene and benzene metabolites on macrophage functions and the ability of macrophages to be activated for functions which are important in host defense. Benzene had no effects on macrophage function or activation for any of the functions tested. Conversely, metabolites of benzene, catechol (CAT), hydroquinone (HQ), benzquinone (BQ), and 1,2,4-benzenetriol (BT) had potent and varied effects on macrophage function and activation. BQ inhibited the broadest range of functions including release of H2O2, Fc receptor-mediated phagocytosis, interferon gamma priming for tumor cell cytolysis, and bacterial lipopolysaccharide (LPS) triggering of cytolysis. BQ was also the most potent metabolite causing inhibition at lower concentrations than the other metabolites. HQ inhibited H2O2 release and priming for cytolysis and BT inhibited phagocytosis and priming for cytolysis. CAT only inhibited the release of H2O2. None of the compounds tested inhibited the induction of class II histocompatibility antigens on the cell surface. All of the effects measured occurred using concentrations of compounds which did not disrupt the cell integrity or inhibit general functions such as protein synthesis. Taken together these data suggest that benzene metabolites alter macrophage function through several mechanisms including inhibition of output enzymes and disruption of signal transduction systems.     

Cytochrome P450 forms in fish: Catalytic,immunological and sequence similarities

1. Hepatocytes isolated from the adult male NMRI mouse or Wistar rat were incubated for 1?h with 0·5 mM ¹⁴C-benzene, the supernatant was separated from the cells, and analysed for benzene metabolites. Separately, formation of sulphate conjugates during benzene metabolism was studied in hepatocytes in the presence of ³⁵S-sulphate. In addition sulphate conjugation of the benzene metabolites hydroquinone and 1,2,4-trihydroxybenzene was investigated in mouse liver cytosol supplemented with 3′-phosphoadenosine-5′-phospho-³⁵S-sulphate.

2. Two novel metabolites, not detectable in rat hepatocyte incubations, were found in mouse hepatocytes, and were identified as 1,2,4-trihydroxybenzene sulphate and hydroquinone sulphate. Formation of the ³⁵S-labelled conjugates could be demonstrated in incubations of mouse liver cytosol with hydroquinone or 1,2,4-trihydroxybenzene supplemented with 3′-phosphoadenosine-5′-phospho-³⁵S-sulphate, and in mouse hepato-cytes incubated with benzene and ³⁵S-sulphate.

3. In comparison with hepatocytes from the Wistar rat, hepatocytes from the NMRI mouse were almost three times more effective in metabolizing benzene. The higher formation of hydroquinone, and the formation of trihydroxybenzene sulphate and hydroquinone sulphate, mainly contributed to the higher rate of benzene metabolism.

4. In conclusion, qualitative and quantitative differences in benzene metabolism may contribute to the higher susceptibility of mouse towards the myelotoxic and leucaemogenic action of benzene.     

Prevention of benzene-induced myelotoxicity and prostaglandin synthesis in bone marrow of mice by inhibitors of prostaglandin H synthase

Administration of benzene to mice causes bone marrow toxicity and elevations in prostaglandin E2 (PGE2), a negative regulator of myelopoiesis. In these experiments, benzene (400 mg/kg; 2 x/day for 2 days) administered to DBA/2 or C57Bl/6 mice decreased bone marrow cellularity and myeloid progenitor cell development (measured as colony-forming units per femur) by 40%. When inhibitors of the cyclooxygenase component of prostaglandin H synthase (PHS) (either indomethacin, 2 mg/kg; aspirin, 50 mg/kg; meclofenamate, 4 mg/kg) were coadministered with benzene, myelotoxicity and the elevation in bone marrow PGE level were prevented. Additionally, when indomethacin (1 microM) was added to cultures of bone marrow cells from benzene-treated mice, myeloid progenitor cell development was the same as the controls. The doses of indomethacin used had no affect on the hepatic conversion of benzene to its major metabolite, phenol. Using purified PHS, indomethacin (10 microM) inhibited the arachidonic acid-dependent oxidation of hydroquinone to p-benzoquinone, a putative reactive metabolite of benzene. Indomethacin (10 microM) had no effect on the H2O2-driven oxidation of hydroquinone catalysed by either PHS-peroxidase or myeloperoxidase. Coadministration of the benzene metabolites, phenol and hydroquinone, has been reported previously to reproduce the myelotoxicity of benzene. In our studies, phenol and hydroquinone (50 mg/kg each; 2 x/day for 2 days) decreased bone marrow cellularity by 40%; however, coadministration of indomethacin (2 mg/kg) or meclofenamate (4 mg/kg) with these metabolites did not prevent the decrease in bone marrow cell number. Our results implicate marrow PHS in mediating the short-term myelotoxicity of benzene.     

Phenol-induced stimulation of hydroquinone bioactivation in mouse bone marrow in vivo: possible implications in benzene myelotoxicity

The coadministration of phenol and hydroquinone has been shown to produce myelotoxicity in mice similar to that observed following benzene exposure. One explanation of this phenomenon may be that phenol enhances the peroxidase-dependent metabolic activation of hydroquinone in the mouse bone marrow. Here we report that radiolabeled [14C]hydroquinone and [14C]phenol bind covalently to tissue macromolecules of blood, bone marrow, liver and kidney, when administered intraperitoneally to the mouse in vivo. Substantially more radiolabeled hydroquinone was covalently bound 18 h after administration as compared with that bound after 4 h. Phenol, when administered together with [14C]hydroquinone, significantly stimulated the covalent binding of [14C]hydroquinone oxidation products to blood (P less than 0.001) and bone marrow (P less than 0.05) macromolecules, but had no significant effect on covalent binding of [14C]hydroquinone oxidation products to liver and kidney macromolecules (P greater than 0.05). Catechol, on the other hand, had no effect on the binding of [14C]hydroquinone oxidation products in either bone marrow, kidney or liver (P greater than 0.05). When hydroquinone was administered together with [14C]phenol, a stimulation of the covalent binding of phenol oxidation products to bone marrow macromolecules also occurred (P less than 0.05). In addition, hydroquinone co-administration increased the covalent binding of [14C]phenol oxidation products in kidney and blood (P less than 0.05), but significantly decreased the covalent binding in liver (P less than 0.05). These results suggest that altered pharmacokinetics play a major role in the hydroquinone-dependent stimulation of covalent binding of [14C]phenol oxidation products to extrahepatic tissue macromolecules in vivo. The mechanism underlying the phenol-induced stimulation of binding of [14C]hydroquinone by phenol in blood and bone marrow remains unclear, but stimulation of peroxidase-mediated hydroquinone metabolism may be responsible. The latter may therefore play an important role in benzene-induced myelotoxicity.     

Inhibition of erythropoiesis by benzene and benzene metabolites

Mice were injected sc with benzene or one of its metabolites, phenol, catechol, or hydroquinone. The ability of these compound to inhibit erythropoiesis was quantified by measuring the incorporation of ⁵⁹Fe into developing erythrocytes. Benzene decreased ⁵⁹Fe incorporation into developing erythrocytes in a dose-dependent manner. Maximum inhibition was observed when benzene was administered 48 hr prior to initiation of the ⁵⁹Fe uptake test. The three metabolites of benzene also significantly inhibited ⁵⁹Fe incorporation when they were administered 48 hr prior to initiation of ⁵⁹Fe uptake assay. The degree of inhibition observed with the metabolites was not as great as that observed with benzene. Coadministration of the microsomal mixed-function oxidase inhibitor, 3-amino-1,2,4-triazole, abolished the erythropoietic toxicity of benzene and phenol but had no effect on the catechol- or hydroquinone-induced toxicity.     

HIGHLIGHT: Dose-Dependent Metabolism of Benzene in Hamsters, Rats, and Mice

The disposition of oral doses of [¹⁴C]benzene was investigatedusing a range of doses that included lower levels (0.02 and0.1 mg/kg) than have been studied previously in rat, mouse,and in hamster, a species which has not been previously examinedfor its capacity to metabolize benzene. Saturation of metabolismof benzene was apparent as the dose increased, and a considerablepercentage of the highest doses (100 mg/kg) was exhaled unchanged.Most of the remainder of the radioactivity was excreted as metabolitesin urine, and significant metabolite-specific changes occurredas a function of dose and species. Phenyl sulfate was the predominantmetabolite in rat urine at all dose levels (64–73%) ofurinary radioactivity), followed by prephenylmercapturic acid(10–11%). Phenyl sulfate (24–32%) and hydroquinoneglucuronide (27–29%) were the predominant metabolitesformed by mice. Mice produced considerably more muconic add(15%), which is derived from the toxic metabolite muconaldehyde,than did rats (7%) at a dose of 0.1 mg/kg. Unlike both ratsand mice, hydroquinone glucuronide (24–29%) and muconicacid (19–31%) were the primary urinary metabolites formedby hamsters. Two metabolites not previously detected in theurine of rats or mice after single doses, 1,2,4-trihydroxybenzeneand catechol sulfate, were found in hamster urine. These dataindicate that hamsters metabolize benzene to more highly oxidized,toxic products than do rats or mice.     

Release of 2-thiobarbituric acid reactive products from glutamate or deoxyribonucleic acid by 1,2,4-benzenetriol or hydroquinone in the presence of copper ions

Cytotoxic effects of various quinone compounds are thought to be due to the formation of semiquinone free radicals. Hydroquinone and 1,2,4-benzenetriol in the presence of copper ions release from glutamate or DNA aldehydic products capable of reacting with 2-thiobarbituric acid (TBA). The formation of TBA reactive products (TBAR) was greater in the presence of 1,2,4-benzenetriol in comparison with hydroquinone. Complete inhibition of formation of TBAR from glutamate by 1,2,4-benzenetriol and copper was observed in the presence of catalase, thiourea and mannitol. Albumin and superoxide dismutase offered substantial protection. Complete protection of formation of TBAR from DNA was observed in the presence of catalase and thiourea. Presence of albumin, mannitol and superoxide dismutase caused only partial inhibition. The formation of TBAR from glutamate or DNA is dependent on copper ion concentration. The present data indicate that hydroquinone and 1,2,4-benzenetriol in the presence of copper ions can lead to the formation of reactive hydroxyl radicals which can release TBAR from glutamate or DNA.     

Homologous recombination initiated by benzene metabolites: a potential role of oxidative stress.

Benzene is a ubiquitous pollutant and known human leukemogen. Benzene can be enzymatically bioactivated to reactive intermediates that can lead to increased formation of reactive oxygen species (ROS). ROS formation can directly induce DNA double-strand breaks, and also oxidize nucleotides that are subsequently converted to double-strand breaks during DNA replication that can be repaired through homologous recombination, which is not error-free. Therefore increased DNA double-strand-break levels may induce hyper-recombination, which can lead to deleterious genetic changes. To test the hypothesis that benzene and its metabolites can initiate hyper-recombination and to investigate the potential role of ROS, a Chinese hamster ovary (CHO) cell line containing a neo direct repeat recombination substrate (CHO 3-6), was used to determine whether benzene or its metabolites phenol, hydroquinone, catechol, or benzoquinone initiated increased homologous recombination and whether this increase could be diminished by the coincubation of cells with the antioxidative enzyme catalase. Results demonstrated that cells exposed to benzene (1, 10, 30, or 100 micro M) for 24 h did not exhibit increased homologous recombination. Increased recombination occurred with exposure to phenol (1.8-, 2.6-, or 2.9-fold), catechol (1.9-, 2-, 5-, or 3.2-fold), or benzoquinone (2.7-, 5.5-, or 6.9-fold) at 1, 10, and 30- micro M concentrations, respectively, and with exposure to hydroquinone at 10 and 30 micro M concentrations (1.5-1.9-fold; p < 0.05). Studies investigating the effects of catalase demonstrated that increased homologous recombination due to exposure to phenol, hydroquinone, catechol, or benzoquinone (10 micro M) could be completely abolished by the addition of catalase. These data support the hypothesis that increased homologous recombination mediates benzene-initiated toxicity and supports a role for oxidative stress in this mechanism.     

Formation of reactive metabolites from benzene

Rat liver mitoplasts were incubated first with [^3H]dGTP, to form DNA labeled in G, and then with [¹⁴C]benzene. The DNA was isolated and upon isopycnic density gradient centrifugation in CsCl yielded a single fraction of DNA labeled with both [^3H] and [¹⁴C]. These data are consistent with the covalent binding of one or more metabolites of benzene to DNA. The DNA was enzymatically hydrolyzed to deoxynucleosides and chromatographed to reveal at least seven deoxyguanosine adducts. Further studies with labeled deoxyadenine revealed one adduct on deoxyadenine. [^3H]Deoxyguanosine was reacted with [¹⁴C]hydroquinone or benzoquinone. The product was characterized using uv, fluorescence, mass and NMR spectroscopy. A proposed structure is described.Dedicated to Professor Dr. med. Herbert Remmer on the occasion of his 65th birthday     

Gender- and Age-Specific Cytotoxic Susceptibility to Benzene Metabolites in Vitro

Benzene, a widely used compound, is a known carcinogen and hematopoietictoxicant. Several studies have shown gender and age differencesin the responses to benzene-induced hematotoxic-ity. It is notknown if these differences in response are due to age-or gender-associatedmetabolic differences or to age- or gender-associated differencesin the susceptibilities of the target cells. In order to addressthis issue, mouse colony-forming units-erythroid (CFU-e, anerythroid precursor cell particularly susceptible to benzenetoxicity) were cultured in the presence of either individualbenzene metabolites or binary mixtures of these metabolites.CFU-e were obtained from unexposed age-matched adult male andfemale (both virgin and pregnant) Swiss Webster (SW) mice andfrom SW male and female 16-day fetuses. The metabolites usedwere phenol, hydroquinone, catechol, benzoquinone, and trans,trans-muconic acid. The concentrations of the individual metabolitesused were 10, 20, and 40 µM. Binary mixtures of metaboliteswere prepared using the lowest concentrations of the individualmetabolites that caused cytotoxicity. These concentrations were10 µM for hydroquinone, catechol, and benzoquinone, and40 µM for phenol and muconic acid. In general, the CFU-efrom adult females (both virgin and pregnant) were more resistantto the toxic effects of the individual metabolites than CFU-efrom other subjects. CFU-e from adult males were more susceptibleto the cytotoxic effects of hydroquinone and benzoquinone thanCFU-e from other subjects and CFU-e from both male and femalefetuses were highly sensitive to the toxic effects of catechol.On the other hand, CFU-e from adult males were less susceptibleto the cytotoxic effects of catechol than CFU-e from other subjects.Similar results were observed with binary mixtures of metabolites.CFU-e from adult males were more susceptible to the binary mixturesthan CFU-e from virgin females and CFU-e from fetal males weremore susceptible than CFU-e from fetal females. In addition,CFU-e from fetuses were more resistant than CFU-e from adultsto the cytotoxic effects of those binary mixtures that did notcontain catechol. In contrast, binary mixtures containing catecholwere more toxic to fetal cells than to adult cells. These resultssuggest that differences in benzene hematotoxicity associatedwith gender and age may be due, at least in part, to intrinsicfactors at the level of the target cell rather than solely toage- or gender-related differences in the metabolism of benzene.