Identification of human cell responses to benzene and benzene metabolites

Benzene is a common air pollutant and confirmed carcinogen, especially in reference to the hematopoietic system. In the present study we analyzed cytokine/chemokine production by, and gene expression induction in, human peripheral blood mononuclear cells upon their exposure to the benzene metabolites catechol, hydroquinone, 1,2,4-benzenetriol, and p-benzoquinone. Protein profiling showed that benzene metabolites can stimulate the production of chemokines, the proinflammatory cytokines TNF-alpha and IL-6, and the Th2 cytokines IL-4 and IL-5. Activated cells showed concurrent suppression of anti-inflammatory cytokine IL-10 expression. We also identified changes in global gene expression patterns in response to benzene metabolite challenges by using high-density oligonucleotide microarrays. Treatment with 1,2,4-benzenetriol resulted in the suppression of genes related to the regulation of protein expression and a concomitant activation of genes that encode heat shock proteins and cytochrome P450 family members. Protein and gene expression profiling identified unique human cellular responses upon exposure to benzene and benzene metabolites.     

Hydrophobicity of benzene

The present work tries to clarify the molecular origin of the poor solubility of benzene in water. The transfer of benzene from pure liquid phase into water is dissected in two processes: transfer from gas phase to pure liquid benzene; and transfer from gas phase to liquid water. The two solvation processes are analyzed in the temperature range 5-100 degrees C according to Lee's Theory. The solvation Gibbs energy change is determined by the balance between the work of cavity creation in the solvent, and the dispersive interactions of the inserted benzene molecule with the surrounding solvent molecules. The purely structural solvent reorganization upon solute insertion proves to be a compensating process. The analysis shows that the work of cavity creation is larger in water than in benzene, whereas the attractive energetic interactions are stronger in benzene than in water; this scenario is true at any temperature. Therefore, both terms act in the same direction, contrasting the transfer of benzene from pure liquid phase into water and determining its hydrophobicity.     

Non-linear production of benzene oxide-albumin adducts with human exposure to benzene

Benzene is initially metabolized to benzene oxide, which either undergoes further metabolism or reacts with macromolecules including proteins. Previously reported levels of benzene oxide-albumin adducts (BO-Alb) are analyzed from 30 workers exposed to 0.2-302 ppm benzene and 43 controls from Shanghai, China. Although both exposed workers and controls had significant levels of BO-Alb in their blood, exposed subjects' adduct levels (GM=378 pmol/g protein) were much greater than those of controls (GM=115 pmol/g protein). When the natural logarithm of the BO-Alb level was regressed upon the natural logarithm of exposure among the 30 exposed subjects, a strong effect of benzene exposure was observed (R(2)=0.612; p<0.0001). Because the slope of the relationship between BO-Alb and benzene exposure was significantly less than one in log-space, we infer that production of benzene oxide was less than proportional to benzene exposure. Since benzene is a substrate for CYP2E1, these results are consistent with saturation of CYP450 metabolism. They indicate that deviations from linear metabolism began at or below benzene exposures of 10 ppm and that pronounced saturation was apparent at 40-50 ppm. To our knowledge, this is the first study to investigate the linearity of human metabolism of a carcinogen based upon protein adducts.     

Blastomogenic effect of benzene

This paper presents a critical review more than 100 references on the possible leukomogenic (blastomogenic) effects of benzene, based upon clinical, epidemiological and experimental dates. The authors came to conclusion that there exist reliable clinical and epidemiological evidences, concerning increased leukomogenic risk on working place with high benzene concentrations in past years (tens and even hundreds of ppm). Most epidemiological studies, indicate now that this risk is also elevated in more favourable working conditions, although practical valuable dose-effect relationship between benzene concentrations and rate of leukomogenic risks is still unknown. Results of experimental investigations on problem of leukomogenic effects of benzene are contradictory. It was stated recently that there is a lack of adequate experimental models of benzene blastomogenesis. Taking into consideration increasing economic significance of benzene and existence of large contingents of workers dealing with benzene, it is necessary to continue appropriate experimental and epidemiological investigations.     

Anaerobic benzene degradation

Although many studies have indicated that benzene persists under anaerobic conditions in petroleum-contaminated environments, it has recently been documented that benzene can be anaerobically oxidized with most commonlyconsidered electron acceptors for anaerobic respiration. These include: Fe(III),sulfate, nitrate, and possibly humic substances. Benzene can also be convertedto methane and carbon dioxide under methanogenic conditions. There is evidencethat benzene can be degraded under in situ conditions in petroleum-contaminatedaquifers in which either Fe(III) reduction or methane production is the predominant terminal electron-accepting process. Furthermore, evidence from laboratory studies suggests that benzene may be anaerobically degraded in petroleum-contaminated marine sediments under sulfate-reducing conditions. Laboratory studies have suggested that within the Fe(III) reduction zone of petroleum-contaminated aquifers, benzene degradation can be stimulated with the addition of synthetic chelators which make Fe(III) more available for microbial reduction. The addition of humic substances and other compounds that contain quinone moieties can also stimulate anaerobic benzene degradation in laboratory incubations of Fe(III)-reducing aquifer sediments by providing an electron shuttle between Fe(III)-reducing microorganisms and insoluble Fe(III) oxides. Anaerobic benzene degradation in aquifer sediments can be stimulated with the addition of sulfate, but in some instances an inoculum of benzene-oxidizing,sulfate-reducing microorganisms must also be added. In a field trial, sulfate addition to the methanogenic zone of a petroleum-contaminated aquifer stimulated the growth and activity of sulfate-reducing microorganisms and enhanced benzene removal. Molecular phylogenetic studies have provided indications of what microorganisms might be involved in anaerobic benzene degradation in aquifers. The major factor limiting further understanding of anaerobic benzene degradation is the lack of a pure culture of an organism capable of anaerobic benzene degradation.     

Metabolism of benzene and phenol in macrophages in vitro and the inhibition of RNA synthesis by benzene metabolites

Benzene may affect hemopoiesis by damaging the bone marrow stroma that provides the microenvironment for hemopoiesis. A possible target of benzene toxicity in the stroma is the macrophage, which is a major source of protein factors required for the proliferation and differentiation of progenitor cells. As an initial approach towards understanding whether benzene inhibits hemopoietic factor production in bone marrow stroma, the metabolism of benzene and phenol has been studied and the effect of benzene and its metabolites on macrophage RNA synthesis has been examined. Benzene is not metabolized in macrophages but phenol, the major metabolite of benzene in bone marrow, is converted by peroxidase in the macrophage to both free metabolites and species which covalently bind to cellular macromolecules. Benzene and its metabolites inhibited RNA synthesis in a dose-dependent manner, with 50% inhibitory concentrations of 5 × 10^–3M for benzene, 2.5 × 10^–3 M for phenol, 2.5 × 10^–5 M for hydroquinone, and 6 × 10^–6 M for p-benzoquinone; this inhibition was not attributable to loss of cell viability. Benzene, possibly by an inhibition of uridine transport into macrophages, and phenol, by its conversion to covalently binding species, inhibit RNA synthesis in macrophages and thus may inhibit the synthesis of colony stimulating factors required for hemopoiesis.Abbreviations CFU-G / M colony forming unit-granulocyte / macrophage - FCS fetal calf serum - IC₅₀ molar concentration causing 50% inhibition - PBS phosphate buffered saline     

Cytogenetic effects of benzene: dosimetric studies on rats exposed to benzene vapour

Rats were exposed to benzene vapour at nominal concentrations in air of 1, 10, 100 and 1000 ppm acutely for 6 h. Bone marrow cells from each animal were examined for chromosomal abnormalities 24 h after the end of the exposure period. This analysis was carried out on 250 metaphases per animal where possible and showed a significant increase in the percentage of cells with chromosomal abnormalities, excluding gaps, in the groups of animals exposed to 100 and 1000 ppm benzene. In the 10-ppm and 1-ppm exposure groups there were elevated levels of cells with abnormalities which showed evidence of being dose-related, although they were not statistically significant.     

Measurement of benzene in the urban area of Naples

The aim of this study is to determine the occurrence of benzene in the air of the city of Naples. A simplified gas-chromatographic method that is sensitive and provides accurate measurements of ambient concentration of benzene has been used. In the centre of Naples the concentration of hydrocarbons depends strongly upon vehicle exhaust.     

Dearomatizing benzene ring reductases

The high resonance energy of the benzene ring is responsible for the relative resistance of aromatic compounds to biodegradation. Nevertheless, bacteria from nearly all physiological groups have been isolated which utilize aromatic growth substrates as the sole source of cell carbon and energy. The enzymatic dearomatization of the benzene nucleus by microorganisms is accomplished in two different manners. In aerobic bacteria the aromatic ring is dearomatized by oxidation, catalyzed by oxygenases. In contrast, anaerobic bacteria attack the aromatic ring by reductive steps. Key intermediates in the anaerobic aromatic metabolism are benzoyl-CoA and compounds with at least two meta-positioned hydroxyl groups (resorcinol, phloroglucinol and hydroxyhydroquinone). In facultative anaerobes, the reductive dearomatization of the key intermediate benzoyl-CoA requires a stoichiometric coupling to ATP hydrolysis, whereas reduction of the other intermediates is readily achieved with suitable electron donors. Obligately anaerobic bacteria appear to use a totally different enzymology for the reductive dearomatization of benzoyl-CoA including selenocysteine- and molybdenum- containing enzymes.     

Matrix interferences in the analysis of benzene in urine

The analysis of benzene in urine of the general population or of exposed workers can be performed with different methods using the ‘purge and trap’ or ‘solid-phase microextraction’ techniques in combination with gas chromatographic analysis and photoionisation or mass spectrometric detection. The published results, however, are deeply conflicting. Differences in sample preparation by different research groups and our own preliminary observations prompted us to investigate pre-analytical and analytical factors potentially capable of modifying the urinary benzene quantification results. Benzene concentrations were measured in 20 urine samples in relation to different conditioning conditions (at 24, 40 and 80°C) and at basic or acid pH. Urinary protein concentrations were measured in the same samples. Urine heating at 80°C yields benzene concentrations on average five times higher than at 24°C. On acidification of urine, the benzene released increases up to 28-fold in comparison to that obtained at uncorrected ‘physiological’ pH. Despite a widely scattered data distribution, a statistically significant linear correlation was found between ‘heat-released’ and ‘acid-labile’ benzene values. There was no correlation between total urinary proteins present in ‘physiological’ concentrations (between 12 and 110 mg/l) and the different kinds of benzene in urine. Our results could perhaps be explained if it is supposed that part of the benzene in urine is absorbed onto sediment, or bound to specific proteins, or derived from parent molecules and is released with pH modification or heat administration. Our observations may also help to explain why the urinary benzene concentrations reported by different investigators vary considerably even when environmental levels are comparable.     

Administration-route-related differences in the micronucleus test with benzene

The effect of route of administration on the outcome of the micronucleus test was studied in 2 laboratories by administering the model chemical benzene intraperitoneally (i.p.) and orally (p.o.) to 2 strains of mice: MS/Ae and CD-1. On the basis of results obtained in a small-scale acute toxicity study and in a pilot micronucleus test, full-scale micronucleus tests were performed with a 24-h sampling time at doses of 250, 500, 1000, and 2000 mg/kg i.p. and 500, 1000, 2000, and 4000 mg/kg p.o. In both strains of mice, a higher incidence of micronucleated polychromatic erythrocytes (MNPCEs) was observed after p.o. administration. The ratio of polychromatic erythrocytes (PCEs) to total erythrocytes decreased more markedly at higher doses i.p. in both strains. Thus, benzene induced more micronuclei via the p.o. route, while inhibitory effects on bone marrow cells were stronger after i.p. administration.     

Thermophilic biofiltration of benzene and toluene

In the current studies, we characterized the degradation of a hot mixture of benzene and toluene (BT) gases by a thermophilic biofilter using polyurethane as packing material and high-temperature compost as a microbial source. We also examined the effect of supplementing the biofilter with yeast extract (YE). We found that YE substantially enhanced microbial activity in the thermophilic biofilter. The degrading activity of the biofilter supplied with YE was stable during long-term operation (approximately 100 d) without accumulating excess biomass. The maximum elimination capacity (1,650 g x m(-3) h(-1)) in the biofilter supplemented with YE was 3.5 times higher than that in the biofilter without YE (470 g g x m(-3) h(-1)). At similar retention times, the capacity to eliminate BT for the YE-supplemented biofilter was higher than for previously reported mesophilic biofilters. Thus, thermophilic biofiltration can be used to degrade hydrophobic compounds such as a BT mixture. Finally, 16S rDNA polymerase chain reaction-DGGE (PCR-DGGE) fingerprinting revealed that the thermophilic bacteria in the biofilter included Rubrobacter sp. and Mycobacterium sp.