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.     

A proposed mechanism of benzene toxicity: Formation of reactive intermediates from polyphenol metabolites

Male Fischer-344 rats were given 100 μCi (14 mg/kg) [¹⁴C]catechol or [¹⁴C]hydroquinone by injection into the lateral tail vein. For a period of at least 24 hr, soluble radioactivity associated with either compound was retained in the bone marrow, but not in the liver or thymus. The amount of covalently bound radioactivity increased with time in all tissues examined and was significantly depressed in liver, white blood cells, and bone marrow in rats pretreated with Aroclor 1254, a regimen which protects against benzene toxicity. Potential enzymatic and nonenzymatic activation pathways for catechol, hydroquinone, and other known benzene metabolites were examined. In air-saturated 50 mm phosphate buffer (pH 7.4) at 37°C, only hydroquinone and 1,2,4-benzenetriol autoxidized. The oxidation product of hydroquinone had an uv absorption maximum (248 nm) identical to that of benzoquinone. With 250 units superoxide dismutase, hydroquinone autoxidation increased fivefold, whereas the oxidation of 1,2,4-benzenetriol was inhibited (4% of control). Epinephrine autoxidation, an indirect measure of superoxide anion generation, was stimulated by 1,2,4-benzenetriol and hydroquinone, but was barely detectable in the presence of catechol. Of the compounds studied, only benzoquinone augmented the oxidation of NADPH by a 3000g rat bone marrow supernatant. These data support a mechanism for benzene toxicity in which the formation of potentially cytotoxic metabolites, semiquinone, and quinone oxidation products and superoxide radicals, result from autoxidation of at least two polyphenol metabolites of benzene, hydroquinone, and 1,2,4-benzenetriol.     

Influences of gender,development, pregnancy and ethanol consumption on the hematotoxicity of inhaled 10 ppm benzene

 The hematotoxic effects of benzene in both humans and animals are well documented. Current estimates concerning the risks associated with benzene exposure are usually based on adult, male cohort studies; however, there are indications that females may respond differently than males to benzene and that fetuses may respond differently than adults. Another factor to be considered in risk estimates is the impact of personal habits. In experimental animals, ethanol consumption is known to increase the hematotoxicity of benzene; therefore, alcohol consumption may also alter the potential risk of individuals exposed to benzene. To address some of the factors that may confound risk estimates for benzene exposure, a series of experiments were performed. Age-matched male as well as pregnant and virgin female Swiss Webster mice were exposed to 10 ppm benzene for 6 h a day over 10 consecutive days (days 6 through 15 of gestation for the pregnant females). Half of the animals also received 5% ethanol in the drinking water during this period. On day 11, bone marrow cells from the adults and liver cells from the fetuses were assayed for the numbers of erythroid colony-forming units (CFU-e). CFU-e assays were also performed on bone marrow cells isolated from 6-week postpartum dams exposed during gestation and from in utero-exposed 6-week old males and females. Gender differences were clearly observed in the responses to the various exposure protocols. Depressions in CFU-e numbers were only seen in male mice while elevations in CFU-e numbers were only seen in female mice. Male mice exposed as adults for 10 days to benzene (B), ethanol (E) or benzene+ethanol (B+E) exhibited depressed CFU-e levels as did male fetal mice exposed to B in utero. In addition, adult male mice which had been exposed in utero to either B or to E individually displayed depressed CFU-e levels. In contrast, none of the groups of female mice exhibited any depressions in CFU-e numbers after any of the exposures. Elevations in CFU-e numbers were observed among pregnant females exposed to E and among adult females exposed to B+E in utero. In summary, a majority (6/9) of the exposure protocols produced depressions in the CFU-e numbers of male mice, whereas a majority (7/9) of the exposure protocols produced no changes in the CFU-e numbers of female mice. Those changes that were observed in females consisted of elevations of CFU-e numbers. These results suggest that the male erythron is more susceptible than the female erythron to the hematotoxicants benzene and ethanol, regardless of whether exposures occur in utero or during adulthood. Received: 21 February 1995 / Accepted: 14 May 1995     

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.     

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.     

Erythroid progenitor cells that survive benzene exposure exhibit greater resistance to the toxic benzene metabolites benzoquinone and hydroquinone

Benzene is a well known hematotoxicant which induces hematopoietic dyscrasias of varying intensities in different individuals and even in different strains of the same experimental animal species. Although there is ample evidence that diverse responses to benzene are related to differences in benzene metabolism, we have recently provided evidence implicating differences in host target cell susceptibility to these diverse responses to benzene. The present study extends our previous work and concerns strain-specific differences in marrow progenitor cells that survive benzene exposure. Two mouse strains (Swiss-Webster and C57Bl/6J) which respond to benzene exposure with different intensities of bone marrow cytotoxicity were used. Bone marrow cells from benzene-exposed and untreated mice were cultured with one of five benzene metabolites: 1,4-benzoquinone (BQ), catechol (C), hydroquinone (HQ), muconic acid (MA) or phenol (P) and the abilities of these cells to produce erythroid (CFU-e) or granulocyte/macrophage colonies (GM-CFU-c) were assessed. In both strains, marrow cells isolated from benzene-exposed mice showed a higher percentage of plated CFU-e surviving culture with BQ, HQ or MA than marrow cells isolated from control mice. In contrast, both strains of benzene-exposed mice displayed decreased percentages of plated CFU-e surviving culture with catechol than cells isolated from control mice. Only one condition (the culturing of cells with HQ under GM-CFU-c forming conditions) showed any strain-specific difference in plating efficiency. In all, 20 possible combinations of benzene metabolites and cell types were examined (5 metabolites × 2 progenitor cell types × 2 strains). With seven of these combinations, the colony-forming efficiencies were higher for plated cells isolated from benzene-exposed mice than from untreated mice. With three combinations, the colony-forming efficiencies were lower for cells from benzene-exposed mice, and for ten combinations, there were no changes in plating efficiencies. Possible mechanisms for an acquired resistance to the toxicities of benzene metabolites were explored by measuring the concentrations of hepatic and bone marrow sulfhydryl (SH) groups in cells isolated from benzene-exposed and untreated mice. In both strains, benzene exposure induced no changes in hepatic SH concentrations, but the SH content of bone marrow was more than doubled after benzene exposure in both strains. These results suggest that a fraction of hematopoietic progenitor cells are able to survive severe benzene exposure and produce progeny because of a marked increase in marrow SH groups which react with electrophilic benzene metabolites. Moreover, this protective mechanism occurs in two mouse strains with differing susceptibilities to benzene. Received: 23 November 1993/Accepted: 26 April 1994     

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.     

Effects of benzene and its metabolites on global DNA methylation in human normal hepatic l02 cells

Benzene is an important industrial chemical that is also widely present in cigarette smoke, automobile exhaust, and gasoline. It is reported that benzene can cause hematopoietic disorders and has been recognized as a human carcinogen. However, the mechanisms by which it increases the risk of carcinogenesis are only partially understood. Aberrant DNA methylation is a major epigenetic mechanism associated with the toxicity of carcinogens. To understand the carcinogenic capacity of benzene, experiments were designed to investigate whether exposure to benzene and its metabolites would change the global DNA methylation status in human normal hepatic L02 cells and then to evaluate whether the changes would be induced by variation of DNA methyltransferase (DNMT) activity in HaeIII DNMT‐mediated methylation assay in vitro. Our results showed that hydroquinone and 1,4‐benzoquinone could induce global DNA hypomethylation with statistically significant difference from control (p < 0.05), but no significant global DNA methylation changes were observed in L02 cells with benzene, phenol, and 1,2,4‐trihydroxybenzene exposure. Benzene metabolites could not influence HaeIII DNMT activity except that 1,4‐benzoquinone shows significantly inhibiting effect on enzymatic methylation reaction at concentrations of 5 μM (p < 0.05). These results suggest that benzene metabolites, hydroquinone, and 1,4‐benzoquinone can disrupt global DNA methylation, and the potential epigenetic mechanism by which that global DNA hypomethylation induced by 1,4‐benzoquinone may work through the inhibiting effects of DNMT activity at 10 μM (p < 0.05). © 2011 Wiley Periodicals, Inc. Environ Toxicol 29: 108–116, 2014.     

Identification of N-acetyl-S-(2,5-dihydroxyphenyl)-L-cysteine as a urinary metabolite of benzene, phenol, and hydroquinone

The metabolite 2-(S-glutathionyl)hydroquinone is formed when a microsomal incubation mixture containing either benzene or phenol is supplemented with glutathione. This metabolite is derived from the conjugation of benzoquinone, an oxidation product of hydroquinone. However, neither the glutathione conjugate or its mercapturate, N-acetyl-S-(2,5-dihydroxyphenyl)-L-cysteine, have been identified as metabolites resulting from in vivo metabolism of benzene, phenol, or hydroquinone. To determine if a hydroxylated mercapturate is produced in vivo, we treated male Sprague-Dawley rats with either benzene (600 mg/kg), phenol (75 mg/kg), or hydroquinone (75 mg/kg) and collected the urine for 24 hr. HPLC coupled with electrochemical detection confirmed the presence of a metabolite that was chromatographically and electrochemically identical to N-acetyl-S-(2,5-dihydroxyphenyl)-L-cysteine. The metabolite was isolated from the urine samples and treated with diazomethane to form the N-acetyl-S-(2,5-dimethoxyphenyl)-L-cysteine methyl ester derivative. The mass spectra obtained from these samples were identical to that of an authentic sample of the derivative. The results of these experiments indicate that benzene, phenol, and hydroquinone are metabolized in vivo to benzoquinone and excreted as the mercapturate, N-acetyl-S-(2,5-dihydroxyphenyl)-L-cysteine.     

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.     

Modifications in the metabolic pathways of benzene in streptozotocin-induced diabetic rat

Benzene is a ubiquitous environmental pollutant primarily metabolized by a cytochrome P-450 (CYP-450) isoenzyme, CYP-450 IIE1. A consistent induction of CYP450 IIE1 has been observed in both rat and human affected by diabetes mellitus. The aim of this study was to evaluate whether streptozotocin (STZ)-induced diabetes determines modifications in the metabolic pathways of benzene in rat. Benzene (100 mg/kg per day, dissolved in corn oil) was administered i.p. once a day for 5 days. Urine samples were collected every day in STZ-treated and normoglycaemic animals, treated and untreated with benzene (n = 10). Urinary levels of trans,trans-muconic acid and of phenol, catechol and hydroquinone (free and conjugated with sulphuryl and glucuronic group) were measured by high-performance liquid chromatography (HPLC). In normoglycaemic rats during the 5 days of treatment with benzene we observed a progressive and significant decrement in the urinary excretion of phenol, phenyl sulphate and glucuronide, catechol, catechol glucuronide, hydroquinone, hydroquinone glucuronide and t,t-muconic acid (P < 0.05). In the diabetic animals, conversely, the same metabolites showed progressively increasing urinary levels (P < 0.05). Catechol sulphate and hydroquinone sulphate levels were below the instrument's detection limit. In the comparison between diabetic and normoglycaemic benzene treated rats, the inter-group difference was significant (P < 0.05) from day 3 of treatment for t,t-muconic acid, and from day 1 for free and conjugated phenol, free and glucuronide catechol and free hydroquinone. In the normoglycaemic rat exposed to benzene the decreasing trend observed in urinary excretion of free and conjugated metabolites may be due to their capability to reduce cytochromial activity. Conversely, in the diabetic rat, urinary levels of benzene metabolites tended to increase progressively, probably due to the consistent induction of CYP-450 IIE1 observed in diabetes, which would overwhelm the inhibition of this isoenzyme caused by phenolic metabolites. Furthermore, the metabolic switch towards detoxification metabolites observed after administration of high doses of benzene is not allowed in the diabetic because of reduced glutathione-S-transferase activity. As a consequence, higher levels of hydroquinone, phenol and catechol, considered the actual metabolites responsibles for benzene toxicity, will accumulate in the diabetic rat. Extrapolating these data to human, we may thus suggest that occupational exposure to benzene of a diabetic subject poses a higher risk level, as his metabolism tends to produce and accumulate higher levels of reactive benzene catabolites. Received: 14 December 1998 / Accepted: 23 March 1999     

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.     

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 the principal hydroxy-metabolites of benzene on microtubule polymerization

The principal hydroxy-metabolites of benzene — phenol, catechol and hydroquinone — possess characteristics and produce toxicity similar to those reported for certain inhibitors of microtubule polymerization. In this study we examined the effects of phenol, catechol and hydroquinone on purified microtubule polymerization and the decay of tubulin-colchicine binding activity. Hydroquinone, but not catechol or phenol, inhibited microtubule polymerization and accelerated the decay of tubulin-colchicine binding activity. The latter effect was shown to be dependent on the concentration of GTP. Hydroquinone did not directly complex with GTP or ATP but bound to the high molecular weight fraction of tubulin. Concentration ratios of hydroquinone to tubulin resulting in altered activity were low, suggesting a specific interaction, presumably at the tubulin-GTP binding site. The acceleration of tubulin-colchicine binding activity decay was completely prevented under anaerobic conditions, indicative of an oxidative mechanism. These studies suggest that hydroquinone, which auto-oxidizes, may interfere with microtubule function, nucleotide binding or both and that this mechanism may be involved in eliciting the wide range of cytoskeletal-related abnormalities observed in cells exposed to benzene in vivo or its metabolites in vitro.     

Acetaminophen and p-Aminophenol Nephrotoxicity in Aging Male Sprague-Dawley and Fischer 344 Rats

Acetaminophen and p-Aminophenol Nephrotoxicity in Aging MaleSprague-Dawley and Fischer 344 rats. TARLOFF, J. B., GOLDSTEIN.R. S., MORGAN, D. G., AND HOOK, J. B. (1989). Fundam Appl Toxicol12, 78–91. Strain differences in susceptibility of ratsto acetaminophen (APAP)-induced nephrotoxicity have been reportedpreviously. Young adult male Fischer 344 (F344) rats are susceptible,whereas weight-matched Sprague-Dawley (SD) rats are not susceptibleto APAP nephrotoxicity. Susceptibility to APAP nephrotoxicityis also age dependent, at least in F344 rats. Middle-aged (12–15months old) male F344 rats are more susceptible to APAP-inducednephrotoxicity than are young adult (2–4 months old) males.APAP nephrotoxicity in aging SD rats has not been evaluated.The present studies were designed to define strain differencesin the nephrotoxicity of APAP and p-aminophenol (PAP), a nephrotoxicmetabolite of APAP, using 2-, 3-, and 9-to 12-month-old F344and SD rats. At 2 months of age, F344, but not SD, rats weresusceptible to APAP-induced nephrotoxicity. However, at 3 monthsof age, strain differences were less marked, as susceptibilityto APAP nephrotoxicity appeared to increase between 2 and 3months of age only in SD rats. By 9–12 months of age,susceptibility to APAP nephrotoxicity was comparable in F344and SD rats. No age- or strain-related differences were observedin the excretory pattern of urinary APAP and metabolites thatmight explain the increased susceptibility of aging rats toAPAP nephrotoxicity. Strain differences in age-matched ratswere not marked for PAP-induced nephrotoxicity. Susceptibilityof both 3-and 12-month- old F344 and SD rats to PAP-inducednephrotoxicity was greater compared to strain-matched 2-month-oldrats. In both F344 and SD rats, PAP nephrotoxicity increasedonly modestly between 3 and 12 months of age, indicating thatincreased susceptibility to PAP probably does not play a majorrole in the age-dependent increase in APAP nephrotoxicity. Thus,strain differences in APAP nephrotoxicity decrease with advancingage. The mechanisms mediating the increased susceptibility toAPAP nephrotoxicity in middle-aged rats are not known but mayrelate, at least in part, to age-dependent differences in pharmacokineties.The present study highlights the importance of considering theage of rats when evaluating drug toxicity. Even in young adultrats, subtle maturational changes in drug metabolism and/ordisposition may occur, making toxicological evaluation in weight-matchedrats of different strains and ages inappropriate.     

Correlation between the induction of micronuclei in bone marrow by benzene exposure and the excretion of metabolites in urine of CD-1 mice

Male and female CD-1 mice received single oral doses of benzene (220, 440, and 880 mg/kg) and were pretreated with modifiers of the mixed-function oxidase enzyme activities. Urinary metabolites (MT) (0-24 and 24-48 hr) were quantified by high-performance liquid chromatography. The micronucleus test was performed at 30 h. The following pretreatments were used to correlate micronucleus formation and the excreted benzene MT: 3-Methylcholanthrene and beta-naphthoflavone led to a marked increase in micronuclei (MN) and MT, whereas phenobarbital caused a slight increase, and SKF-525A had no effect. MN and MT were decreased when benzene was administered by the ip route or toluene was given simultaneously. Females had a lower number of MN and excreted more unconjugated phenol than did males. Muconic acid, hydroquinone, and phenol glucuronide and MN correlated well. They were dependent on both the dose and route of administration of benzene, being most inducible by P-448 inducers, in males more than females. The administration of hydroquinone induced MN, but phenol or catechol (200, 250, and 150 mg/kg, po, respectively) did not, and none of these compounds yielded trans, trans-muconic acid, a benzene MT in urine. This study establishes that benzene myeloclastogenicity is a function of its metabolism and that quantification of urinary metabolites could provide reliable correlates of this effect in vivo.     

Catechol and hydroquinone have different redox properties responsible for their differential DNA-damaging ability.

We examined the redox properties of the "carcinogenic" catechol and the "noncarcinogenic" hydroquinone in relation to different DNA damaging activities and carcinogenicity using 32P-labeled DNA fragments obtained from the human genes. In the presence of endogenous NADH and Cu2+, catechol induces stronger DNA damage than hydroquinone, although the magnitudes of their DNA damaging activities were reversed in the absence of NADH. In both cases, DNA damage resulted from base modification at guanine and thymine residues in addition to strand breakage induced by Cu+ and H2O2, generated during the oxidation of catechol and hydroquinone into 1,2-benzoquinone and 1,4-benzoquinone, respectively. EPR and 1H NMR studies indicated that 1,2-benzoquinone is converted directly into catechol through a nonenzymatic two-electron reduction by NADH whereas 1,4-benzoquinone is reduced into hydroquinone through a semiquinone radical intermediate through two cycles of one-electron reduction. The reduction of 1,2-benzoquinone by NADH proceeds more rapidly than that of 1,4-benzoquinone. This study demonstrates that the rapid 1,2-benzoquinone two-electron reduction accelerates the redox reaction turnover between catechol and 1,2-benzoquinone, resulting in the enhancement of DNA damage. These results suggest that the differences in NADH-mediated redox properties of catechol and hydroquinone contribute to their different carcinogenicities.     

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.