Variability of albumin adducts of 1,4-benzoquinone,a toxic metabolite of benzene,in human volunteers

Abstract

A putative haematotoxic and leukaemogenic metabolite of benzene, 1,4-benzoquinone (1,4-BQ), reacts rapidly with macromolecules. The authors previously characterized levels of the albumin (Alb) adduct (1,4-BQ-Alb) of this reactive species in populations of workers exposed to benzene. Since high levels of 1,4-BQ-Alb were also measured in unexposed workers from those investigations, the current study was initiated to determine potential sources of 1,4-BQ in the general population. A single blood sample was collected from 191 healthy subjects from the Research Triangle area, NC, USA, to determine the baseline 1,4-BQ-Alb levels and contributing sources. The median 1,4-BQ-Alb at baseline was 550?pmol?g^?1 Alb (interquartile range 435–814?pmol?g^?1). A second blood sample was collected approximately 3 months later from a subgroup of 33 subjects to estimate the within- and between-person variation in 1,4-BQ-Alb. Standardized questionnaires were administered to collect information about demographic, dietary and lifestyle factors. Multiple linear regression models identified several significant contributors to 1,4-BQ-Alb levels, including gender, body mass index (BMI), the gender–BMI interaction, automobile refuelling, smoking status, and consumption of fruit and the artificial sweetener, aspartame. The authors predicted that these background levels of 1,4-BQ-Alb were equivalent to occupational exposures between 1 and 3 parts per million of benzene. Mixed effects linear models indicated that the random variation in adduct levels was about equally divided between and within subjects. The observations indicate that levels of 1,4-BQ-Alb cover a wide range in the general population, and they support the hypotheses that demographic, diet and lifestyle factors are contributing sources.     

Using liquid chromatography–tandem mass spectrometry to quantify monohydroxylated metabolites of polycyclic aromatic hydrocarbons in urine

We present an assay which employs enzyme digestion and solid phase extraction followed by liquid chromatography–tandem mass spectrometry to simultaneously quantify 16 hydroxylated polycyclic aromatic hydrocarbons (OHPAHs) in 3-ml samples of urine. The analytes consisted of 2-, 3-, and 4-ring OHPAHs, namely, 1- and 2-hydroxynaphthalene (1- and 2-OHNAP), 2-hydroxyfluorine (2-OHFLU), 1-, 2-, 3-, 4-, and 9-hydroxyphenanthrene (1-, 2-, 3-, 4-, and 9-OHPHE), 1-hydroxypyrene (1-OHPYR), 1- and 2-hydroxybenzo(a)anthracene (1- and 2-OHBAA), 3- and 6-hydroxychrysene (3- and 6-OHCHR) and 3-, 7-, and 9-hydroxybenzo(a)pyrene (3-, 7-, and 9-OHBAP). The method was validated using urine samples from steel workers and control subjects. The coefficients of variation of the method for the particular analytes were between 7% and 27% and the limits of quantitation were between 0.002 and 0.010 μg/l urine. The 2- and 3-ring OHPAHs were easily quantified in all subjects. However, 1-OHPYR was the only representative of the 4- and 5-ring metabolites that could be quantified. Pairwise correlations showed that all OHPAHs were highly correlated with each other (0.553 ≤ r ≤ 0.910) and with 1-OHPYR (0.614 ≤ r ≤ 0.910), the metabolite most widely accepted as a short-term biomarker of exposure to PAHs. The analyte, 2-OHNAP exhibited the lowest pairwise correlations with the other OHPAHs (0.542 ≤ r ≤ 0.628), presumably due to confounding by smoking. Metabolites of phenanthrene, an abundant PAH and the smallest to possess a bay region, are promising OHPAHs for characterizing both exposures to PAHs and the various metabolic pathways.     

Determination of dihydroxynaphthalenes in human urine by gas chromatography-mass spectrometry

A gas chromatography-mass spectrometry (GC-MS) method was developed for measuring 1,2-dihydroxynaphthalene (1,2-DHN) and 1,4-dihydroxynaphthalene (1,4-DHN) in urine. The method involves enzymatic digestion of urinary conjugates to release the DHNs which were then analyzed as trimethylsilyl derivatives by GC-MS. For 1,2-DHN and 1,4-DHN, respectively, the assay limits of detection were 0.21 and 0.15 microg/l, the assay limits of quantitation were 0.69 and 0.44 microg/l, and the coefficients of variation were 14.7 and 10.9%. This method was successfully applied to determine urinary levels of 1,2-DHN and 1,4-DHN in coke workers (14 top workers and 13 side-bottom workers) and 21 matching control workers from the steel industry of northern China. The geometric mean (GM) levels of 1,2-DHN were approximately 100 and 30 times higher than those of 1,4-DHN in exposed and control subjects, respectively. The GM levels 1,2-DHN and 1,4-DHN were significantly higher for coke workers (1,2-DHN: top workers--552 microg/l, side-bottom workers--260 microg/l; 1,4-DHN: top workers--3.42 microg/l, side-bottom workers--3.56 microg/l) than for controls (1,2-DHN: 38.8 microg/l; 1,4-DHN: 1.21 microg/l) (por=0.623; p<0.0001). Also, levels of 1,2-DHN were significantly correlated with those of serum albumin adducts of l,2-naphthoquinone (rs=0.492, p=0.0004). These results indicate that 1,2- and 1,4-DHN are good biomarkers for assessment of naphthalene exposure in coke workers. Since the DHNs are precursors of the naphthoquinones, which have been implicated as toxic products of naphthalene metabolism, measurements of urinary DHNs may have toxicological significance.     

Evidence for the formation of Michael adducts from reactions of (E,E)-muconaldehyde with glutathione and other thiols

Glutathione induces the rapid isomerization of (Z,Z)-muconaldehyde to (E,E)-muconaldehyde via (E,Z)-muconaldehyde, probably via reversible Michael addition of the thiol to one of the enal moieties of the muconaldehyde. Reactions of (E,E)-muconaldehyde with glutathione (in the presence and absence of equine glutathione S-transferase), phenylmethanethiol, N-acetyl-l-cysteine, and N-acetyl-l-cysteine methyl ester were investigated using mass spectrometric techniques. In each case, evidence was obtained for the formation of Michael adducts, e.g., reaction between (E,E)-muconaldehyde and glutathione gave 4-glutathionyl-hex-2-enedial and 3,4-bis-glutathionyl-hexanedial. These experiments suggest that (Z,Z)-muconaldehyde, a putative metabolite of benzene, could lead to the long established urinary metabolite of benzene, (E,E)-muconic acid, via glutathione-mediated isomerization to (E,E)-muconaldehyde.     

Rapid determination of six urinary benzene metabolites in occupationally exposed and unexposed subjects

A gas chromatography-mass spectrometry method for measurement of the main urinary metabolites of benzene, namely, phenol, catechol, hydroquinone, 1,2,4-trihydroxybenzene (trihydroxybenzene), t,t-muconic acid (muconic acid), and S-phenylmercapturic acid (phenylmercapturic acid), is reported. The method is considerably simpler than existing assays. It was applied to urine from benzene-exposed subjects and controls from Shanghai, China. When subjects were divided into controls (n = 44), those exposed to 31 ppm benzene (n = 19), Spearman correlations with exposure category were >/= 0.728 (p < 0.0001) for all metabolites except trihydroxybenzene. When exposed subjects were compared on an individual basis, all metabolites, including trihydroxybenzene, were significantly correlated with benzene exposure (Pearson r >/= 0.472, p /= 0.708, p < 0.0001). Ratios of individual metabolite levels to total metabolite levels provided evidence of competitive inhibition of CYP 2E1 enzymes leading to increased production of phenol, catechol, and phenylmercapturic acid at the expense of hydroquinone, trihydroxybenzene, and muconic acid. Since all metabolites were detected in all control subjects, the method can be applied to persons exposed to environmental levels of benzene.     

Characterization of metabolic activation of pentachlorophenol to quinones and semiquinones in rodent liver

Pentachlorophenol (PCP), a widely used biocide, induces liver tumors in mice but not in rats. Metabolic activation of PCP to chlorinated quinones and semiquinones in liver cytosol from Sprague-Dawley rats and B6C3F1 mice was investigated in vitro (1) with microsomes in the presence of either beta-nicotinamide adenine dinucleotide phosphate (NADPH) or cumene hydroperoxide (CHP), (2) with CHP in the absence of microsomes, and (3) with horseradish peroxidase (HRP) and H2O2. Mono-S- and multi-S-substituted adducts of tetrachloro-1,4-benzoquinone (Cl4-1,4-BQ) and Cl4-1,2-BQ and their corresponding semiquinones [i.e. tetrachloro-1,4-benzosemiquinone (Cl4-1,4-SQ) and tetrachloro-1,2-benzosemiquinone (Cl4-1,2-SQ)] were measured by gas chromatography-mass spectrometry (GC-MS). Qualitatively, the metabolites of PCP were the same in both rats and mice for all activation systems. Induction of PCP metabolism by either 3MC or PB-treated microsomes was observed in NADPH- but not in CHP-supported systems. In rats, the amount of induction was comparable with either 3MC or PB. 3MC was a stronger inducer than PB in mice and also induced a greater amount of metabolism than in rats. This suggests that induction of specific P450 isozymes may play a role in the toxicity of PCP to mice. Both HRP/H2O2 and CHP led to production of the full spectrum of chlorinated quinones and semiquinones, confirming the direct oxidation of PCP. CHP (with or without microsomes) converted PCP into much greater quantities of quinones and semiquinones than did microsomal P450/NADPH or HRP/H2O2 in both species. This implies that, under conditions of oxidative stress, endogenous lipid hydroperoxides may increase PCP metabolism sufficiently to enhance the toxicity and carcinogenicity of PCP.     

Simultaneous determination of urinary 1- and 2-naphthols, 3- and 9-phenanthrols,and 1-pyrenol in coke oven workers

A method was developed for simultaneous quantification of urinary 1- and 2-naphthols, 3- and 9-phenanthrols and 1-pyrenol using gas chromatography with mass spectrometry (GC-MS). This method was applied to urine samples from coke oven workers (n =28) and controls (n =22) from Northern China. Geometric mean levels of urinary 1-naphthol (58.8 μg l^?1), 2-naphthol (34.1 μg l^?1), 3-phenanthrol (7.35 μg l^?1), 9-phenanthrol (1.28 μg l^?1) and 1-pyrenol (25.4 μg l^?1) were significantly higher among coke oven workers than controls. All the substances tested were highest among top-of-oven workers, who had 15-fold higher 1-naphthol, eight-fold higher 2-naphthol and 20-fold higher 1-pyrenol levels compared with controls. Using multiple linear regression models, 72.5% of the variation in 1- and 2-naphthol and 82.8% of the variation in 1-pyrenol were explained by the concentration of naphthalene or pyrene in the urine, the work category and the smoking intensity. Cigarette consumption significantly contributed to levels of urinary 1-pyrenol and naphthols, particularly 2-naphthol. A negative relationship between work category and the ratio of naphthols/1-pyrenol was observed among smokers. Our results suggest that urinary naphthols and phenanthrols reflect polycyclic aromatic hydrocarbon (PAH) exposure as well as the widely used 1-pyrenol, and that interactions between cigarette smoking and PAH exposure result in different patterns of metabolism for individual PAHs.     

An integrated approach to biomonitoring exposure to styrene and styrene-(7,8)-oxide using a repeated measurements sampling design

Abstract

The aim of this work was to investigate urinary analytes and haemoglobin and albumin adducts as biomarkers of exposure to airborne styrene (Sty) and styrene-(7,8)-oxide (StyOX) and to evaluate the influence of smoking habit and genetic polymorphism of metabolic enzymes GSTM1 and GSTT1 on these biomarkers. We obtained three or four air and urine samples from each exposed worker (eight reinforced plastics workers and 13 varnish workers), one air and urine samples from 22 control workers (automobile mechanics) and one blood sample from all subjects. Median levels of exposure to Sty and StyOX, respectively, were 18.2 mg m^?3 and 133 µg m^?3 for reinforced plastics workers, 3.4 mg m^?3 and 12 µg m^?3 for varnish workers, and <0.3 mg m^?3 and <5 µg m^?3 for controls. Urinary levels of styrene, mandelic acid, phenylglyoxylic acid, phenylglycine (PHG), 4-vinylphenol (VP) and mercapturic acids (M1+M2), as well as cysteinyl adducts of serum albumin (but not those of haemoglobin) were significantly associated with exposure status (controls相似文献   

Investigation of benzene oxide in bone marrow and other tissues of F344 rats following metabolism of benzene in vitro and in vivo.

This study examines the initial activation of benzene, exploring key aspects of its metabolism by measurement of benzene oxide (BO) and BO-protein adducts in vitro and in vivo. To assess the potential influence of various factors on the production of BO, microsomes were prepared from tissues that were either targets of benzene toxicity, i.e. the bone marrow and Zymbal glands, or not targets, i.e. liver and kidneys, of control and acetone-treated F344 rats. No BO or phenol was detected in microsomal preparations of bone marrow or Zymbal glands (less than 0.007 nmol BO/mg protein and 0.7 nmol phenol/mg protein). On the other hand, BO and phenol were readily detected in preparations of liver and kidney microsomes and acetone pretreatment resulted in a 2-fold (kidney) increase or 3.7-fold (liver) increase in production of these metabolites. Initial rates of BO production in the liver isolates were 30 (control) to 50 (acetone-treated) times higher than in the corresponding kidney tissues. The estimated half-life of BO in bone marrow homogenates was 6.0 min and the second-order reaction rate constant was estimated to be 1.35 x 10(-3) l (g bone marrow)(-1) (h)(-1). These kinetic constants were used with measurements of BO-bone marrow adducts in F344 rats, receiving a single gavage dosage of 50-400 mg benzene (kg body weight)(-1) (McDonald, T.M., et al. (1994), Cancer Res. 54, 4907-4914), to predict the bone marrow dose of BO. Among the rats receiving 400 mg (kg body weight) (-1), a BO dose of 1.13 x 10(3) nM BO-h was estimated for the bone marrow, or roughly 40% of the corresponding blood dose predicted from BO-albumin adducts. Together these data suggest that, although BO is not produced at detectable levels in the bone marrow or Zymbal glands of F344 rats, BO is rapidly distributed via the bloodstream to these tissues where it may play a role in toxicity.     

Hemoglobin and albumin adducts of naphthalene-1,2-oxide, 1,2-naphthoquinone and 1,4-naphthoquinone in Swiss Webster mice

The toxicity of naphthalene in rodents has been attributed to the reactive metabolites naphthalene-1,2-oxide (NPO), 1,2-naphthoquinone (1,2-NPQ) and 1,4-naphthoquinone (1,4-NPQ). Differences in the formation of these reactive metabolites in different species can shed light on the mechanism by which naphthalene exerts its toxicity. Protein adducts allow investigators to study the disposition of reactive metabolites that cannot be measured directly. We measured cysteinyl adducts of the above metabolites in hemoglobin (Hb) and albumin (Alb) from the blood of male Swiss Webster mice dosed with 1.56-200mg naphthalene/kg b.w. Levels of NPO adducts (designated as NPO1-Hb, NPO2-Hb, NPO1-Alb and NPO2-Alb) increased nonlinearly with the administered dose; levels of Alb adducts were higher than those of Hb adducts; levels of NPO1 adducts were higher than those of NPO2 adducts. Levels of NPQ adducts (1,2-NPQ-Alb, 1,4-NPQ-Alb, 1,2-NPQ-Hb and 1,4-NPQ-Hb) were lower than those of NPO. Although NPQ-Alb increased with doses above 12.5 mg naphthalene/kg body wt. (b.w.), levels of NPQ-Hb barely increased above the background levels within the dose range examined. The shapes of the dose response curves for total cysteinyl adducts (combined NPO and NPQ) in Hb and Alb were consistent with previous results of radiobinding experiments in naphthalene-dosed mice. Dose-specific levels of NPO-Alb remained essentially constant in mice over the dose range of 25-200 mg/kg b.w. while those of 1,2- and 1,4-NPQ-Alb diminished over this range. Comparing dose-specific levels of NPO-Alb in Swiss Webster mice with those published previously in F344 rats suggests that glutathione depletion in mice occurred at about 1/8th the administered dose previously observed in rats. This suggests that mice could be more susceptible than rats to the toxic effects of naphthalene due to more pronounced depletion of glutathione at a given dose.