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Analysis of OSHA's short-term-exposure limit for benzene.

A review of the data cited by OSHA in its final standard for exposure to benzene provides no clear scientific basis for a short-term-exposure limit (STEL). While leukemia and bone marrow toxicity were related to cumulative exposures of benzene received by workers, no evidence was presented that the rate of exposure at a given cumulative exposure contributed to the effects. Likewise, animal experiments suggested that exposures of several hours duration at a given level of benzene induced more bone-marrow toxicity when administered 3 rather than 5 days/week but did not indicate that the rate of exposure over shorter time scales played any role. The toxicokinetics of benzene in humans were also studied to determine whether nonlinear dose-rate effects would be likely to result from peak exposures associated with an exposure dose of 8 ppm-hr, which is allowed under the permissible exposure limit. This led to three conclusions. First, the concentration of benzene in the bone marrow should be sufficiently damped that the impact of a peak exposure should be minimal. Second, the peak concentration of benzene in the liver should be within the capacity of the cytochrome P450 system to maintain first-order metabolism. And finally, the maximum blood concentration of metabolites should be well below levels which have been shown to induce toxic effects in vitro. Taken together, the toxicokinetic relationships and the absence of clear experimental dose-rate effects suggest that the current STEL for benzene is unwarranted, assuming that 8-hr average exposures are kept below 1 ppm. While the argument can be made, on the basis of health considerations, that the existing 8-hr limit for benzene is too high, the rate of exposure during short periods appears to be irrelevant. Thus, we recommend that health professionals focus upon long-term exposures to benzene received by large numbers of workers rather than devote scarce resources to evaluate transient air levels.

Animals↗

An overview of published benzene exposure data by industry in China, 1960-2003.

This article presents an overview of occupational benzene exposures in China based on data published in Chinese medical journals. The data were derived from 384 reports of benzene poisoning or industrial hygiene surveys published in Chinese medical journals between 1960 and 2003. The following information was extracted whenever available: industry, occupation, task, date, benzene levels, sampling location, workplace descriptions and, for case reports, medical diagnosis. Each paper provided one or more sets of benzene data, each set representing a sampling location or job title with one to several measurements including, mainly, breathing zone area concentration measurements, and much less frequently personal monitoring. Two criteria based on data quality were applied to select suitable data for analyses. The selected exposure data were analyzed by industry and time period. Nine hundred five sets of benzene measurements from 72 industries were reported in the 384 papers selected for this review, and 621 sets (68.6%) presented average benzene concentrations, which covered 55 industries. The distribution of the reported average benzene exposures was skewed with a median of 51.5 mg/m3. The average benzene concentrations were below 100 mg/m3 for 406 (65%) of the 621 reported average concentrations. The medians of the reported averages in mg/m3 for the five industries with the highest exposures were: 124.8 for leather products, 98.7 for electronic devices, 75.4 for machinery, 50.4 for shoes, and 50.3 for office supplies and sports equipment manufacturing. These data describe the concentrations and changing patterns of occupational benzene exposure by industry and time period in China.

Air Pollutants, Occupational↗

Clinical analysis of 43 cases of chronic benzene poisoning.

Benzene can result in bone marrow suppression. Chronic benzene poisoning (CBP) can be found among workers with excessive benzene exposure. CBP could give the appearance of different types of disorders such as leukopenia, agranulocytosis, anemia, pancytopenia, aplastic anemia (AA), myelodysplastic syndrome (MDS), and leukemia. This paper describes 43 CBP cases with the patients' ages ranging from 18 to 36 years (average: 23 years). Among them, 13 (30%) were male and 30 (70%) were female. Their job titles were furniture maker, shoemaker, industrial painter and metal shop worker. Their work durations ranged from 1.5 to 72 months (average: 14 months). Benzene levels in these workplaces exceeded 30 mg/m3. Ten of the 43 cases (23%) were diagnosed as mild cases of CBP, another 10 (23%) were moderate, and 23 (53%) were severe. Treatment for CBP included the following: cessation of benzene exposure, general supportive therapy, antibiotics, vitamins, corticosteroids, androgens, colony-stimulating factors (G-CSF, GM-CSF), blood component therapy, and traditional Chinese medicine. Thirty-three (77%) of the cases recovered completely, nine (21%) cases improved, and one (2%) died. In general, prognosis of CBP cases is optimistic when appropriate treatment is given. However, a few of the benzene-induced AA cases showed no response to treatment, which raises questions about the traditional view of the pathogenesis of the illness. Furthermore, only a part of the population with the same level of benzene exposure would suffer from the disease. Still, CBP cases with the same benzene exposure level exhibited different extents of severity of the illness. This evidence suggests strongly the existence of individual susceptibility. Detection of the biological markers regarding the individual susceptibility would be valuable for screening workers who are not suitable to be exposed to benzene.

Adolescent↗

Thioredoxin overexpression in mice, model of attenuation of oxidative stress, prevents benzene-induced hemato-lymphoid toxicity and thymic lymphoma.

OBJECTIVE: Reactive oxygen species (ROS), generated following benzene exposure, are considered to trigger the development of hematopoietic neoplasms, although little supporting evidence has been found. In this study, we examined whether the experimental elimination of ROS generated following benzene exposure prevents the development of benzene-induced hematopoietic disorders to clarify the mechanism underlying the development of benzene-induced hematopoietic disorders. METHODS: C57BL/6 mice, overexpressing human thioredoxin (h-Trx-Tg), were used to examine the possible nullification of ROS induction following benzene exposure. The experimental group was exposed to 300 ppm benzene 6 hours/day, 5 days/week, for 26 weeks, and lifetime observation followed by molecular and histopathological examinations were carried out. RESULTS: The present study using h-Trx-Tg mice showed a complete suppression of the development of thymic lymphoma induced by benzene inhalation (0% in h-Trx-Tg vs 30% in wild-type (Wt) mice). This was associated with a 48% decrease in the incidence of clastogenic micronucleated reticulocyte induction in the h-Trx-Tg mice compared with the Wt control after 2 weeks of inhalation. As underlying mechanisms, the attenuation of oxidative stress was accompanied by a complete abrogation of hemato-lymphoid toxicity, as shown by the upregulation of the activity of superoxide-dismutase, and a consequently stable ROS level, as determined by cell sorting using 2', 7'-dichlorodihydrofluorescein diacetate, along with a significant attenuation of the overexpression of a cell cycle-dependent kinase inhibitor, p21. CONCLUSION: The attenuation of benzene-induced oxidative stress and that of the consequent lymphomagenesis were observed for the first time, and these indicate a role of oxidative stress in benzene-induced clastogenesis and lymphomagenesis. (These attenuations were not seen in nonthymic lymphomas, and no leukemias developed in C57BL/6 used in this study.) During the constitutive overexpression of h-Trx, the expression of aryl-hydrocarbon receptor in h-Trx-Tg mice was downregulated, which may also contribute to the attenuation.

Animals↗

Exposure assessment of benzene in Thai workers, DNA-repair capacity and influence of genetic polymorphisms.

Exposure to benzene can cause DNA damage and the subsequent development of cancer. In this study, study subjects were 31 laboratory workers at a petrochemical factory and 31 gasoline service attendants. Control subjects were 34 workers from a mail sorting service center. Occupational exposures to benzene were assessed using biomarkers of exposure in blood and urine. Induction of DNA-repair capacity was assessed as a biomarker of early effect. The effects of polymorphisms in a metabolizing gene (CYP2E1), in detoxification genes (NQO1 and GSTT1), and in a DNA-repair gene (XRCC1, codon 399) on biomarker levels were evaluated. The mean individual benzene exposure of laboratory workers (24.40+/-5.82 ppb) and that of gasoline service attendants (112.41+/-13.92 ppb) were significantly higher than in controls (1.39+/-0.17 ppb, p<0.001). Blood benzene levels of laboratory workers (169.12+/-30.60 ppt) and gasoline service attendants (483.46+/-59.62 ppt) were significantly higher than those of the controls (43.30+/-4.89 ppt, p<0.001). Trans,trans-muconic acid levels in post-shift urine samples collected from laboratory workers (0.14+/-0.02 mg/g creatinine) and gasoline service attendants (0.20+/-0.02 mg/g creatinine) were significantly higher than in urine samples of controls (0.04+/-0.01 mg/g creatinine, p<0.001). The level of benzene exposure was correlated with blood benzene levels (R2=0.65, p<0.01) and post-shift urinary trans,trans-muconic acid concentrations (R2=0.49, p<0.01). As a biomarker of early effect, DNA-repair capacity was assessed by use of the cytogenetic challenge assay, i.e., chromosomal aberrations in peripheral lymphocytes were assessed after challenging blood cultures with 1 Gy gamma radiation. A significantly lower DNA-repair capacity--determined as dicentrics in laboratory workers (0.17 per metaphase cell) and in gasoline service attendants (0.19 per metaphase cell) compared with controls (0.12 per metaphase cell, p<0.001)--was observed. The frequency of deletions in laboratory workers (0.22 per metaphase cell) and gasoline service attendants (0.39 per metaphase cell) were significantly higher than in control workers (0.16 per metaphase cell, p<0.01 and p<0.001, respectively). An increase in radiation-induced dicentrics and deletions indicate a lower DNA-repair capacity in benzene-exposed workers. The influence of genetic polymorphisms on the biomarkers was assessed. Benzene-exposed workers who carried CYP2E1*1/*5 or *5/*5 genotypes excreted slightly higher levels of trans,trans-muconic acid than workers who carried the CYP2E1*1/*1 genotype. In this study, NQO1 and GSTT1 genotypes did not have any effect on the levels of trans,trans-muconic acid. In the case of XRCC1, laboratory workers with 399Arg/Gln or Gln/Gln had a lower DNA-repair capacity--measured as radiation-induced frequency of dicentrics and deletions--than those with the 399Arg/Arg genotype (p<0.01). Our results show that biomarkers of internal dose and early biological effect in people occupationally exposed to benzene are influenced by genetic polymorphisms in susceptibility genes.

Benzene↗

Urban benzene exposure and oxidative DNA damage: influence of genetic polymorphisms in metabolism genes.

Benzene has been implicated as an environmental risk factor in leukaemia and other haematological diseases. Relationships between urban benzene exposure, oxidative DNA damage and polymorphisms in metabolism enzymes were examined in 40 volunteers living and working in Copenhagen. Personal exposures to benzene, toluene and methyl tert-butyl ether (MTBE) were monitored during a 5-day period. DNA damage was measured by 7-hydro-8-oxo-2'-deoxyguanosine (8-oxodG) in lymphocyte DNA and urine and by comet assay with use of fapyguanine glycosylase (FPG) and endonuclease III (ENDO). Excretion of the benzene metabolites trans,trans-muconic acid (ttMA) and S-phenylmercapturic acid (S-PMA) were measured in urine. Polymorphisms in glutathione-S-transferases T1 (GSTT1), M1 (GSTM1) and P1 (GSTP1) and NAD(P)H:quinone oxidoreductase (NQO) were determined. Median exposures to benzene, toluene and MTBE were 2.5, 18.7 and 0.86 microg/m(3). No significant correlations between external benzene exposure and any of the biomarkers were found. However, a significant correlation between S-PMA excretion and 8-oxodG in lymphocytes was found (R(s)=0.39). Men were found to excrete significantly more ttMA than the women did and ttMA excretion in men was found to be significantly associated with external benzene exposure (R=0.53, P=0.025). In addition, ttMA and S-PMA excretion was significantly higher in subjects with the NQO+/-genotype compared with subjects with the wild type (P=0.004 and P=0.011, respectively). Even though there are some limitations in this study due to the low range of benzene exposure and biomarker concentrations as well as a small number of subjects, these results could suggest that even at ambient concentrations exposure to benzene could have genotoxic effects in susceptible individuals.

Adult↗

Effect of sorbic acid administration on urinary trans,trans-muconic acid excretion in rats exposed to low levels of benzene.

Trans,trans-muconic acid (t,t-MA) is a biomarker of benzene exposure reflecting metabolic activation to trans,trans-muconaldehyde. t,t-MA background urinary levels are highly variable, thus limiting its use to exposure monitoring of levels over 1 ppm of benzene. Actually, sorbic acid (SA) is known to influence background excretion of t,t-MA in man, but only a few examples suggest that SA ingestion can enhance t,t-MA levels occurring together with benzene exposure. In this study, the effect of SA was investigated in benzene-exposed male Sprague-Dawley rats exposed to 1 ppm benzene for 6 h. Exposed animals had a 24-h urinary t,t-MA excretion higher than that observed in non-exposed animals (87+/-13 microg/kg vs 19+/-3 microg/kg body weight). The oral dose of 8 mg/kg body weight SA had no effect on urinary t,t-MA both in control and in benzene-exposed rats. Increases of t,t-MA levels in urine occurred at SA doses of 50-200 mg/kg body weight, and co-exposure to benzene and SA (50 and 100 mg/kg body weight) produced additive enhancement of t,t-MA excretion. These data demonstrate the dose-response relationship between SA administration and t,t-MA excretion. Our study showed that SA ingestion at doses equal to or greater than 50 mg/kg body weight significantly affects the t,t-MA urinary levels in rats exposed to 1 ppm of benzene for 6 h. These data support the conclusion that in man t,t-MA is not suitable for biomonitoring of low levels of benzene exposure.

Animals↗

Effects of benzene on splenic, thymic, and femoral lymphocytes in mice.

Chronic exposure to high concentrations of benzene, primarily by inhalation, can affect the function of the human immune system. Limited data are available on the immunotoxic effects of low concentrations of benzene. This study evaluated the effects of 1, 5, 10, 100, and 200 ppm benzene on lymphocytes in mice exposed by inhalation for up to 8 weeks. Exposure to 100 or 200 ppm benzene induced rapid and persistent reductions in femoral B-, splenic T- and B-, and thymic T-lymphocytes. The percentage of femoral B-lymphocytes and thymic T-lymphocytes in apoptosis was increased 6- to 15-fold by 200 ppm benzene compared to controls. Replication of femoral B-lymphocytes was increased during the exposure period in the bone marrow as a compensation for the lymphocyte loss induced by 100 and 200 ppm benzene. Exposure of mice to 10 ppm benzene or less did not have a statistically significant effect on numbers or replication of the lymphocyte populations evaluated. A reduced number of splenic B-lymphocytes after 2 weeks of exposure to benzene appeared to be the most sensitive end point and time point for evaluating benzene cytotoxicity in this study.

Administration, Inhalation↗

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 degrees C) and at basic or acid pH. Urinary protein concentrations were measured in the same samples. Urine heating at 80 degrees C yields benzene concentrations on average five times higher than at 24 degrees 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.

Artifacts↗

Micronucleus induction in mice exposed to diazoaminobenzene or its metabolites, benzene and aniline: implications for diazoaminobenzene carcinogenicity.

Diazoaminobenzene (DAAB), a manufacturing intermediate metabolized primarily to the known carcinogens benzene and aniline, has been identified as an impurity in a number of dyes and coloring agents that are components of cosmetics, food products, and pharmaceuticals. Several structural analogs of DAAB are carcinogenic as well. DAAB was selected for metabolism and toxicity studies by the National Toxicology Program (NTP) based on the potential for human exposure, positive Salmonella data, and lack of adequate toxicological data. In the toxicology studies in mice, DAAB exhibited properties similar to benzene and aniline. Because both these metabolites induce micronuclei (MN) in rodent bone marrow erythrocytes, DAAB was tested for induction of micronuclei in male B6C3F(1) mice. DAAB was administered twice by corn oil gavage at 24 h intervals, at doses of 25, 50, and 100 mg/kg per day. In addition, comparative micronucleus tests were conducted with benzene, aniline, and a mixture of benzene plus aniline; doses were based on the respective molar equivalents of each metabolite to DAAB. It was hypothesized that any observed increase in micronuclei seen in DAAB-treated mice would be due primarily to the effects of the benzene metabolite, as benzene is a more potent inducer of chromosomal damage than aniline. Results of this study showed that DAAB and benzene were effective inducers of micronuclei, with stronger responses noted for DAAB at higher doses. Positive results were also obtained with the mixture of benzene and aniline, although the magnitude of the response was lower than for DAAB. Aniline gave a weak positive response at doses exceeding its molar equivalent to 100 mg/kg DAAB. Overall, the data indicated that DAAB is a potent inducer of micronuclei in mice, and its activity appears to be closely related to the activity of benzene, one of its primary metabolites. The results are consistent with a prediction of carcinogenicity for DAAB.

Aniline Compounds↗

Benzene: a secondary pollutant formed in the three-way catalyst.

Benzene emissions from a relevant proportion of today's gasoline-driven passenger cars and light-duty vehicles can increase by up to 2 orders of magnitude when driving at high engine load (e.g., on highways). Under such conditions, post-catalyst benzene levels exceeded those found pre-catalyst. As a consequence, formation of benzene in the catalyst was postulated. To further reduce ambient air concentrations of benzene,these critical operating conditions must be carefully avoided. Here, we report in detail to what extent and at what operating conditions catalyst-induced benzene and toluene formation can occur. For that purpose, a EURO-1 passenger car (1.8 L, model year 1995)fulfilling the valid regulations, equipped with a new, two-layered, Pd-CeO2-Al2O3/Rh-ZrO2-Al2O3 three-way catalyst was operated at steady state on a chassis dynamometer at 100, 125, and 150 km/h at variable air to fuel ratios. Pre- and post-catalyst exhaust gas concentrations of benzene, toluene, C2-, and C3-benzenes were monitored at a time resolution of 0.5 Hz by means of chemical ionization mass spectrometry. A net benzene formation window, ranging from pre-catalyst exhaust gas temperatures of 600-730 degrees C and lambda-values of 0.83-0.95, with a pronounced minimum at 0.87, was observed. Dealkylation reactions of aromatic hydrocarbons are assumed to be the major pathway leading to benzene.

Air Pollutants↗

Effects of reformulated gasoline and motor vehicle fleet turnover on emissions and ambient concentrations of benzene.

Gasoline-powered motor vehicles are a major source of toxic air contaminants such as benzene. Emissions from light-duty vehicles were measured in a San Francisco area highway tunnel during summers 1991, 1994-1997, 1999, 2001, and 2004. Benzene emission rates decreased over this time period, with a large (54 +/- 5%) decrease observed between 1995 and 1996 when California phase 2 reformulated gasoline (RFG) was introduced. We attribute this one-year change in benzene mainly to RFG effects: 36% from lower aromatics in gasoline that led to a lower benzene mass fraction in vehicle emissions, 14% due to RFG effects on total nonmethane organic compound mass emissions, and the remaining 4% due to fleet turnover. Fleet turnover effects accumulate over longer time periods: between 1995 and 2004, fleet turnover led to a 32% reduction in the benzene emission rate. A approximately 4 microg m(-3) decrease in benzene concentrations was observed at a network of ambient air sampling sites in the San Francisco Bay area between the late 1980s and 2004. The largest decrease in annual average ambient benzene concentrations (1.5 +/- 0.7 microg m(-3) or 42 +/- 19%) was observed between 1995 and 1996. The reduction in ambient benzene between spring/summer months of 1995 and 1996 due to phase 2 RFG was larger (60 +/- 20%). Effects of fuel changes on benzene during fall/winter months are difficult to quantify because some wintertime fuel changes had already occurred prior to 1995.

Air Pollutants↗

Experimental and quantum-chemical determination of the (2)H quadrupole coupling tensor in deuterated benzenes.

Deuterium Quadrupole Coupling Constant (DQCC) in benzene was determined both experimentally by Nuclear Magnetic Resonance spectroscopy in Liquid Crystalline solutions (LC NMR) and theoretically by ab initio electronic structure calculations. DQCCs were measured for benzene-d(1) and 1,3,5-benzene-d(3) using several different liquid crystalline solvents and taking vibrational and deformational corrections into account in the analysis of experimental dipolar couplings, used to determine the orientational order parameter of the dissolved benzene. The experimental DQCC results for the isotopomers benzene-d(1) and 1,3,5-benzene-d(3) are found to be 187.7 kHz and 187.3 kHz, respectively, which are essentially equal within the experimental accuracy (+/-0.4 kHz). Theoretical results were obtained at different C-D bond lengths, and by applying corrections for electron correlation and rovibrational motion on top of large-basis-set Hartree-Fock results. The computations give a consistent DQCC of ca. 189 kHz for three different isotopomers; benzene-d(1), 1,3,5-benzene-d(3), and benzene-d(6), revealing that isotope effects are not detectable within the present experimental accuracy. Calculations carried out using a continuum solvation model to account for intermolecular interaction effects result in very small changes as compared to the data obtained in vacuo. The comparison of theoretical and experimental results points out the selection of the underlying molecular geometry as the most likely source of the remaining discrepancy of less than 2 kHz. Such an agreement between the calculated and the experimental DQCC results can only be achieved if rovibrational effects are considered on one hand in the experimental direct dipolar coupling data, and on the other hand in the theoretical property calculation, as is done presently.

Benzene↗

Benzene metabolism by the isolated perfused lung.

Benzene is an occupational hazard and environmental toxicant whose toxic effects are dependent on its metabolism by cytochrome P-450. Most physiologically based pharmacokinetic models assume that benzene is metabolized only in the liver. They may not be completely accurate in predicting metabolism, especially following inhalation exposure, if metabolism by the lung is important. In the current study, the metabolizing capability of the lung was examined in an in vivo simulation using the isolated perfused lung. Lungs from the rabbit, rat, and mouse were used to mimic benzene metabolism following exposure via the pulmonary vasculature. With the isolated perfused mouse lung, three concentrations (55 microM, 120 microM, and 200 microM) were used to evaluate concentration dependence. To evaluate the ability of the lung to metabolize inhaled benzene, the isolated perfused mouse lung was exposed to benzene (approximately 175 ppm) via the trachea. Benzene was metabolized in all species, with phenol being the major metabolite. Phenylsulfate was also detected in perfusate from rabbits and mice but at much lower levels. Benzene metabolism was concentration dependent in mice. The ability of the lung to metabolize benzene during inhalation exposure was demonstrated in the isolated perfused mouse lung. These results demonstrate that the lung can metabolize benzene in an in vivo simulation when exposed via the pulmonary vasculature or via inhalation.

Air Pollutants, Occupational↗

Reevaluation of benzene exposure for the Pliofilm (rubberworker) cohort (1936-1976).

The Pliofilm cohort is the most intensely studied group of workers chronically exposed to benzene. Information on this cohort has been the basis for regulations and/or guidelines for occupational and environmental exposure to benzene. Rinsky et al. (1986, 1987) and Crump and Allen (1984) developed different approaches for reconstructing the exposure history of each member of the group. The predicted levels of exposure, combined with the data on the incidence of disease, have been used to estimate benzene's carcinogenic potency. In this paper, recent information from worker interviews and historical records from the National Archives and elsewhere were used to evaluate the accuracy of prior exposure estimates and to develop better ones for the cohort. The following factors were accounted for: (1) uptake of benzene due to short-term, high-level exposure to vapors, (2) uptake due to background concentrations in the manufacturing building, (3) uptake due to contact with the skin, (4) morbidity and mortality data on workers in the Pliofilm process, (5) the installation of industrial hygiene engineering controls, (6) extraordinarily long work weeks during the 1940s, (7) data indicating that airborne concentrations of benzene were underestimated due to inaccurate monitoring devices and the lack of adequate field calibration mated due to inaccurate monitoring devices and the lack of adequate field calibration of these devices, and (8) likely effectiveness of respirators and gloves. Our estimates suggest that Crump and Allen (1984) overestimated the exposure of workers in some job classifications and underestimated others, and that Rinsky et al. (1981, 1986) almost certainly underestimated the exposure of nearly all workers. Airborne concentrations of benzene at the St. Marys facility during the years of its operation were found (on average) to be about half those of the two Akron facilities. Our analysis indicates that short-term, high-level exposure to benzene vapors and dermal exposure significantly increased (by about 25-50%) the total absorbed dose of benzene for some workers. One of the key findings was that, unlike prior analyses, the three facilities probably had significantly different airborne concentrations of benzene, especially during the 1940s and 1950s.

Air Pollutants, Occupational↗

Biomarkers of human exposure to benzene.

Three biomarkers for benzene exposure were developed. The first biomarker, muconic acid in urine, results from the ring opening of a benzene metabolite. A gas chromatography/mass spectroscopy (GC/MS) assay was developed to measure urinary muconic acid, and the analyte in urine samples from workers occupationally exposed to benzene was determined. Workers exposed to benzene concentrations as low as 4.4 ppm over an 8-h day showed higher urinary muconic acid concentrations than did any control individual (p < .005). The second biomarker, S-phenylcysteine (SPC) in hemoglobin (Hb), results from the addition of benzene oxide to a cysteine sulfhydryl group. A GC/MS assay was developed to measure SPC in the blood of F344/N rats and B6C3F1 mice exposed to benzene by inhalation. The cysteine moiety on rat Hb is at a more accessible site than on Hb of mice or humans, and rats showed considerably higher levels of SPC than did mice. As yet, we have been unable to detect SPC in the globin of humans occupationally exposed to benzene. The third biomarker is SPC in albumin. In humans occupationally exposed to average concentrations of 0, 4.4, 8.4, and 23.1 ppm benzene, 8 h/d, 5 d/wk, SPC increased in the exposed groups linearly, giving a statistically significant slope (p < .001) of 0.044 +/- 0.008 pmol/mg albumin/ppm. The assay for SPC is arduous and often imprecise; assuming these difficulties can be overcome, muconic acid in urine and SPC in albumin may be useful for accurately determining benzene exposure.

Administration, Inhalation↗

Partition coefficients for benzene in human skin.

The contribution of benzene to body burden after skin absorption compared with that due to inhalation absorption is of potential interest in the setting and interpretation of benzene (inhalation) exposure standards. However, an understanding of the quantitative relationship between skin and inhalation absorption, under different exposure conditions, is required. Such knowledge may be gained through physiological based pharmacokinetic (PBPK) modeling. The intake of benzene to the body via inhalation has been studied extensively. Physiological parameters enabling the calculation of amounts of benzene entering the blood stream per unit time are readily available for use in a PBPK model. Unfortunately, some data (i.e., partition coefficients) that would enable biologically plausible calculation of amounts of benzene entering the blood stream via skin absorption in a PBPK model are not available. Hence, the aim of this research was to determine partition coefficients across the epidermal and dermal layers of human skin so that these could be used within a PBPK model to determine quantitatively the flow rate of benzene per unit time through intact skin into the blood stream. The partition coefficients found for blood substitute: viable epidermis and blood substitute: dermis were, respectively, 2.4 and 11.2. Partition coefficients for benzene : stratum corneum (4.2), whole skin : blood substitute (2.2), benzene : water (109/126), and benzene : blood substitute (55/59) also were determined for the purposes of validating the blood substitute: viable epidermis and blood substitute : dermis partition coefficients.

Benzene↗

The nature of chromosomal aberrations detected in humans exposed to benzene.

Benzene is an established cause of human leukemia that is thought to act by producing chromosomal aberrations and altered in cell differentiation. In several recent studies increased levels of chromosomal aberrations in peripheral blood lymphocytes were correlated with a heightened risk of cancer, especially hematological malignancies. Thus, chromosomal aberrations may be a predictor of future leukemia risk. Previous studies exploring whether benzene exposure induces chromosomal aberrations have yielded mostly positive results. However, it remains unclear whether the chromosomal aberrations induced by benzene occur in a distinct pattern. Here, we thoroughly review the major chromosome studies published to date in benzene-exposed workers, benzene-poisoned and preleukemia patients, and leukemia cases associated with benzene expose. Although three cytogenetic markers (chromosomal aberrations, sister chromatid exchanges, and micronuclei) are commonly examined, our primary focus is on studies of chromosomal aberrations, because only this marker has so far been correlated with increased cancer risk. This review surveys the published literature, analyzes the study results, and discusses the characteristics of effects reported. In most studies of currently exposed workers, increases in chromosomal aberrations were observed. However, due to the relatively small number of affected individuals and variability in the reported aberrations, firm conclusions cannot be made about the involvement of specific chromosomes or chromosome regions. Further, in leukemia cases associated with benzene exposure, there is no evidence of a unique pattern of benzene-induced chromosomal aberrations in humans. Leukemia cases associated with benzene exposure are, however, more likely to contain clonal chromosome aberrations then those arising de novo in the general population.

Adult↗