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Cancer Epidemiology Biomarkers & Prevention Vol. 13, 1631-1639, October 2004
© 2004 American Association for Cancer Research

Effects of Genetic Polymorphisms of Metabolic Enzymes on Cytokinesis-Block Micronucleus in Peripheral Blood Lymphocyte among Coke-Oven Workers

Shuguang Leng1, Yufei Dai1, Yong Niu1, Zufei Pan2, Xiaohua Li1, Juan Cheng1, Fengsheng He1 and Yuxin Zheng1

1 National Institute for Occupational Health and Poison Control, Chinese Center for Disease Control and Prevention, Beijing, China and 2 Institute of Industrial Health, Benxi Steel Industrial Corp., Benxi, Liaoning, China

Requests for reprints: Yuxin Zheng, National Institute for Occupational Health and Poison Control, Chinese Center for Disease Control and Prevention, 29 Nanwei Road, Beijing, China 100050. Phone: 86-10-83132515; Fax: 86-10-63182372. E-mail: yxzheng{at}163bj.com


    Abstract
 Top
 Abstract
 Introduction
 Materials and Methods
 Results
 Discussion
 References
 
Exploring the associations between genetic polymorphisms of metabolic enzymes and susceptibility to polycyclic aromatic hydrocarbon (PAH)–induced chromosomal damage is of great significance for understanding PAH carcinogenesis. Cytochrome P450, glutathione S-transferase, microsomal epoxide hydrolase, NAD(P)H:quinone oxidoreductase, and N-acetyltransferase are PAH-metabolizing enzymes. In this study, we genotyped for the polymorphisms of these genes and assessed their effects on cytokinesis-block micronucleus (CBMN) frequencies in peripheral blood lymphocytes among 141 coke-oven workers and 66 non–coke-oven worker controls. The geometric means of urinary 1-hydroxypyrene levels in coke-oven workers and the controls were 12.0 and 0.7 µmol/mol creatinine, respectively (P < 0.01). The CBMN frequency (number of micronuclei per 1,000 binucleated lymphocytes) was significantly higher in coke-oven workers (9.5 ± 6.6{per thousand}) than in the controls (4.0 ± 3.6{per thousand}; P < 0.01). Among the coke-oven workers, age was positively associated with CBMN frequency; the mEH His113 variant genotype exhibited significantly lower CBMN frequency (8.5 ± 6.5{per thousand}) than did the Tyr113/Tyr113 genotype (11.3 ± 6.4{per thousand}; P < 0.01); the low mEH activity phenotype exhibited a lower CBMN frequency (8.6 ± 6.8{per thousand}) than did the high mEH activity phenotype (13.2 ± 6.7{per thousand}; P = 0.01); the GSTP1 Val105/Val105 genotype exhibited a higher CBMN frequency (15.0 ± 5.8{per thousand}) than did the GSTP1 Ile105/Ile105 or Ile105/Val105 genotypes (9.3 ± 6.5{per thousand}; P < 0.01); the joint effect of high mEH activity phenotype and GSTM1 null genotype on CBMN frequencies was also found. Gene-environment interactions between occupational PAH exposure and polymorphisms of mEH and/or GSTM1 were also evident. These results indicate that the mEH, GSTP1, and GSTM1 polymorphisms may play a role in sensitivity or genetic susceptibility to the genotoxic effects of PAH exposure in the coke-oven workers.


    Introduction
 Top
 Abstract
 Introduction
 Materials and Methods
 Results
 Discussion
 References
 
Chemicals present in the coal-coking process has been classified as class I carcinogens by IARC (1), and there has been sufficient epidemiologic evidence suggesting an etiologic link between carcinogenic polycyclic aromatic hydrocarbon (PAH) exposure and lung cancer risk in coke-oven workers (2, 3). Although a high level of PAH exposure may be confined to occupational workers, cigarette smoking and air pollution are important sources of environmental PAHs in the general population. Therefore, the metabolite 1-hydroxypyrene (1-OHP) in urine, a major metabolite of pyrene, has been found to be a golden internal exposure index of recent exposure to PAHs in both occupational and environmental settings (4).

Most PAHs require metabolic activation and detoxification by different enzymes that contribute to their ultimate mutagenic and carcinogenic effects (5). In general, carcinogenic PAHs, such as benzo(a)pyrene [B(a)P], need to be activated by the phase I enzymes (e.g., cytochrome P450 1A1 and 2E1) to form ultimate carcinogens, such as B(a)P diol epoxide (BPDE), whereas the phase II enzymes (e.g., glutathione S-transferases and N-acetyltransferases) generally mediate the conjugation of water-soluble moieties, such as glutathione, which are responsible for detoxification of these reactive metabolites (6). The microsomal epoxide hydrolase (mEH) converts trans-7,8-diol of B(a)P to more water-soluble trans-dihydrodiols, which is further activated by phase I enzymes to form the ultimate carcinogenic diol epoxide (BPDE; ref. 7). NAD(P)H:quinone oxidoreductase 1 could detoxify the quinone-reactive intermediates of PAHs to protect against formation of PAH-DNA adducts (8). However, the genes encoding these enzymes are highly polymorphic and many polymorphisms in these genes with functional significance have been found to modify individual susceptibility to PAH carcinogenesis (e.g., lung cancer; ref. 9).

The cytokinesis-block micronucleus (CBMN) assay could detect chromosome breakage and loss specifically in cells that have completed nuclear division once (10, 11) and has emerged as a maturing biomarker of chromosomal damage relevant to cancer in recent years (12, 13). Because chromosome damage is an important early biological event in chemical carcinogenesis, exploring the relationship between genetic variants of metabolic enzymes and PAH-induced chromosomal damages is important for our understanding of PAH carcinogenesis and improvement of risk assessment.

Numerous studies have investigated the effects of polymorphisms in genes involved in activation or detoxification of carcinogens on phenotypic biomarkers of exposure, mainly urinary 1-OHP, DNA or protein adducts, and urinary mutagenicity in populations occupationally exposed to PAHs (14-24). For example, several studies have found consistent associations between the GSTM1 null genotype and increased levels of urinary mutagen excretion (25), DNA adducts (15, 17, 19, 20, 22), and BPDE-serum albumin levels (21) and between low mEH activity genotype/phenotype and lower levels of urinary mutagenicity, DNA adducts, and BPDE-serum albumin adducts (16, 26). However, there are few studies addressing the impact of polymorphisms in metabolic genes on biomarkers of early effects in occupationally PAH-exposed populations (23, 27, 28) and some published results are conflicting. No published studies have investigated the relationship between genotypes of metabolic enzymes and the frequencies of CBMN induced by exposure to occupational PAHs that are common in coke-oven workers.

In this study, we genotyped for several metabolic genes involved in PAH metabolism, determined personal PAH exposure (expressed as urinary 1-OHP), and investigated their relationships with the frequencies of CBMN in peripheral blood lymphocyte among 141 coke-oven workers and 66 non–coke-oven workers.


    Materials and Methods
 Top
 Abstract
 Introduction
 Materials and Methods
 Results
 Discussion
 References
 
Study Population and Sample Collection
All study participants were employed in a steel company in northeast China. Employees (n = 141) working with the same coke-oven, who had been exposed to coke-oven emissions regularly and had been employed for at least 6 months, were recruited into this study as the exposed group. Sixty-six medical staffs, working in the affiliated hospital of the company located ~3 km away from the coking area, were recruited as the nonexposure controls, because no obvious work-related PAH exposure was found for these medical staffs. Exclusion criteria for participation in the study included recent treatment with mutagenic agents (such as X-ray), chronic conditions (such as autoimmune diseases), and recent acute infections that required medications such as antibiotics. After an informed consent was obtained, all participants were interviewed by an occupational physician using a detailed questionnaire including demographic information, smoking history, alcohol consumption, history of occupational exposure, and personal medical history. Individuals who had smoked >100 cigarettes in their lifetime were considered as smokers and asked for information on a variety of smoking-related questions. Among these smokers, individuals who still smoked when interviewed were classified as current smokers; the others were classified as former smokers. Individuals who drank more than twice a week in the last 6 months were classified as alcohol users.

Spot urine samples were obtained from each subject at the end of a work shift after at least 4 consecutive days of work, maintained at –20°C, and used later for the measurement of urinary 1-OHP. Three milliliters of venous blood samples were drawn from each subject, of which 1 mL was treated with heparin as anticoagulant for immediate culture of CBMN assay and 2 mL was anticoagulated with EDTA and stored at –20°C for extraction of DNA.

The research protocol was approved by the Research Ethics Committee of the National Institute for Occupational Health and Poison Control, Chinese Center for Disease Control and Prevention.

PAH Exposure Assessment
Airborne PAHs in the working environment of coke-oven and non–coke-oven workers were sampled ~1.5 month before urine and blood sample collection by the static air sampling method and analyzed with the OSHA method no. 58 (29). The levels of benzene-soluble matter (BSM) were gravimetrically determined and particulate-phase B(a)P levels were analyzed by high-performance liquid chromatography with a fluorescence detector ({lambda}ex = 365 nm, {lambda}em = 405 nm).

The excretion of 1-OHP as the internal dose of personal recent PAH exposure was measured according to the method of Jongeneelen et al. (30) with some modifications (31) described as follows. Briefly, instead of using ß-glucuronidase hydrolysis, thawed urine specimen (2 mL) was mixed with 15 mol/L NaOH solution (0.5 mL) and incubated at 100°C for 3.5 hours for hydrolyzation. Carbazole (10 µg/mL, 50 µL), as an internal standard, was added into the urine specimen, and the urine samples were adjusted to pH 3.0 to 5.0 with HCl. Extraction was done with CH2Cl2 (4 mL) and the organic solvent was evaporated to dryness under a stream of nitrogen. The residue was reconstituted in 0.2 mL of 75% methanol and 10 µL was injected onto a C18 column. The analyte was eluted at a flow rate of 1 mL/min with a mobile phase of 75% methanol. The 1-OHP was detected by a fluorescence detector ({lambda}ex/{lambda}em, 346/386 nm). Figure 1 presents a typical high-performance liquid chromatogram of 1-OHP with carbazole as an internal standard from a top-of-oven worker. Quantification was based on peak height ratios of the 1-OHP to the carbazole. The limit of detection was 0.1 µg/L urine (signal-to-noise = 3). Measurements below the limit of detection (for four non–coke-oven workers only) were replaced with prior to statistical analysis, where LOD is limit of detection (32). Quality control samples were assayed together with each batch of measurements. The recovery from the entire procedure was 94.0% at 5 µg/L and 99.5% at 20 µg/L. The intraday relative SD values were 6.2% and 5.8% at 5 and 20 µg/L, respectively, and the interday relative SD values were 7.7% and 8.9% at 5 and 20 µg/L, respectively (n = 6 for each group). The urinary 1-OHP concentrations were corrected by urinary creatinine and presented as µmol/mol creatinine.



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Figure 1. High-performance liquid chromatogram of urinary 1-OHP obtained from an exposed subject (a top-of-oven worker).

 
CBMN Assay Using Peripheral Blood Lymphocytes
The CBMN assay was done according to the standard method as described previously (10, 11). Duplicate lymphocyte cultures were set up immediately after blood collection. Forty-four hours after PHA stimulation, cytokinesis was blocked with 6 µg/mL cytochalasin-B, and 28 hours later, lymphocytes were harvested. Hypotonic treatment was used and cells were fixed with methanol and acetic acid at 4:1 before being transferred to slides. Standard scoring criteria (10, 33) for selecting binucleated cells and identifying a micronucleus were adopted. All slides were coded and scored blindly by an experienced scorer. A total of 1,000 binuleated lymphocytes were examined for detection of micronuclei for each subject.

Genotyping
DNA was isolated from the whole blood using a standard method (34). The Ile/Val polymorphism in exon 7 of the CYP1A1 was analyzed according to the method of Hayashi et al. (35). The DraI polymorphism in intron 6 and PstI polymorphism in the 5'-flanking region of CYP2E1 were genotyped by the methods of Stephens et al. (36) and Kato et al. ((37), respectively. Analysis of the GSTP1 polymorphism resulting in an Ile/Val substitution at residual 105 in exon 5 was done as described by Saarikoski et al. (38). Detection of the C/T 609 (Pro187Ser) polymorphism of NQO1 was conducted according to the method of Chan et al. (39). The genotypes of GSTM1 and GSTT1 were determined by a modified multiplex PCR method with ß-globin as positive control (40, 41). For NAT2, KpnI, TaqI, and BamHI polymorphisms were determined and classified as fast or slow acetylators according to the method of Hickman and Sim (42). The Tyr/His polymorphism at residual 113 in exon 3 and His/Arg polymorphism at residual 139 in exon 4 of mEH was analyzed as described by Zhou et al. (43). All genotypes were evaluated and agreed upon by at least two persons independently. Ten percent of DNA samples were genotyped a second time and the concordance was 100%.

Statistical Analysis
Student's t tests were used to compare age and the ln-transformed urinary 1-OHP levels between two exposure populations and compare the ln-transformed urinary 1-OHP levels between current and noncurrent smokers (former and never smokers). Mann-Whitney U tests were used to compare the air levels of PAHs, cigarettes per day, and CBMN frequencies between non–coke-oven workers and coke-oven workers and to compare the CBMN frequencies between the categories of selected variables (age, sex, coking history, and smoking and alcohol status). {chi}2 test was used to compare the frequencies of current smokers and alcohol users between two exposure populations. Spearman rank correlation test was used to evaluate the relationship between urinary 1-OHP concentrations and CBMN frequencies. For multivariate analysis, the CBMN data were ln transformed to normalize the variance. The differences in ln-transformed CBMN data between each genotype of single metabolic gene and between each combination of mEH phenotypes and GSTM1 genotypes were analyzed with multivariate analysis of covariance with adjustment for urinary 1-OHP, age, sex, and cigarettes per day in exposed and nonexposed groups separately. For genotypes or genotype combinations with more than two levels in multivariate analysis, dummy variables for genotypes or genotype combinations were designed. To give a convenient summary of the CBMN results in the tables, means and SDs of the nontransformed CBMN data were presented; for urinary 1-OHP, geometric means and their 95% confidence intervals were used. All statistical tests were two sided ({alpha} = 0.05) and done using Statistical Analysis System software (version 8.0; SAS Institute, Inc., Cary, NC).


    Results
 Top
 Abstract
 Introduction
 Materials and Methods
 Results
 Discussion
 References
 
The demographic data and environmental exposure information of coke-oven workers and non–coke-oven workers are summarized in Table 1. The distributions of age, sex, and prevalence of drinking were not significantly different between the two exposure groups, but the percentages of current smokers and number of cigarettes smoked per day were higher in coke-oven workers than in non–coke-oven workers (P < 0.01). The medians of air BSM and particulate-phase B(a)P were significantly higher in coke-oven (BSM, 328.6 µg/m3 and B(a)P, 926.9 ng/m3, n = 30) than in non–coke-oven working environment (BSM, 97.8 µg/m3 and B(a)P, 49.1 ng/m3, n = 10; P < 0.01; Table 1) with the highest at the top of oven (BSM, 1,233.3 µg/m3 and B(a)P, 2,634.9 ng/m3, n = 10). The geometric mean of urinary 1-OHP was significantly higher in coke-oven workers (12.0; 95% confidence interval, 10.4-13.9 µmol/mol creatinine) than in non–coke-oven workers (0.7; 95% confidence interval, 0.6-1.3 µmol/mol creatinine; Table 1) and significantly higher in current smokers than in noncurrent (former and never) smokers in both exposure groups (coke-oven workers, 13.8 versus 9.4 µmol/mol creatinine, P = 0.01 and non–coke-oven workers, 1.0 versus 0.5 µmol/mol creatinine, P < 0.01, respectively) as well as higher in male workers than in female workers (coke-oven workers, 12.5 versus 8.5 µmol/mol creatinine, P = 0.09 and non–coke-oven workers, 0.7 versus 0.5 µmol/mol creatinine, P = 0.03).


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Table 1. Demographic data of coke-oven and non–coke-oven workers in a Chinese occupational population

 
Table 2 shows the results of CBMN frequencies and the stratification analysis by age, sex, smoking and alcohol status, and coking history. The median CBMN frequency was 9.5 ± 6.6{per thousand} in coke-oven workers, which was significantly higher than that in non–coke-oven workers (4.0 ± 3.6{per thousand}; P < 0.01). In coke-oven workers, subjects with age ≥44 years had significantly higher CBMN frequencies (11.3 ± 6.6{per thousand}) than those with age 35 to 44 years (8.8 ± 5.7{per thousand}; P = 0.05) and those with age <35 years (8.6 ± 7.2{per thousand}; P = 0.02). We further analyzed the association between age and CBMN frequencies using multivariate analysis of covariance with adjustment for coking history in coke-oven workers and found a similar result (P = 0.04 for difference of CBMN frequencies between age >44 and <35 groups). In non–coke-oven workers, the subjects with age >44 years also had higher CBMN frequencies (4.7 ± 5.1{per thousand}) than younger groups, but the differences were not significantly. We did not find any statistically significant association between coking history and CBMN frequencies in coke-oven workers. Female subjects had higher CBMN frequencies than male subjects in coke-oven workers, but the difference was not statistically significant even with adjustment of age (P = 0.27), and there was no sex difference in the non–coke-oven workers. No differences in CBMN frequencies between current smokers and noncurrent smokers and between alcohol users and nonalcohol users in both exposure groups were found even with adjustment of age and sex (data not shown). The differences in CBMN frequencies between coke-oven workers and non–coke-oven workers in subgroups by age, sex, and smoking and alcohol status remained significantly different by Mann-Whitney U test. In all subjects, correlation between urinary 1-OHP concentrations and CBMN frequencies was statistically significant (n = 207, Spearman r = 0.383; P < 0.01); however, this significant correlation disappeared when analyzed for coke-oven workers and non–coke-oven workers separately (data not shown).


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Table 2. CBMN frequencies ({per thousand}) by age, sex, smoking and alcohol status, and coking history in coke-oven and non–coke-oven workers

 
The effects of genotypes of phase I and II metabolic enzymes on CBMN frequencies are presented in Tables 3 and 4. Using multivariate analysis of covariance with adjustment for urinary 1-OHP, age, sex, and cigarettes per day, coke-oven workers carrying the Tyr113/Tyr113 genotype in exon 3 of mEH had significantly higher CBMN frequencies than those with the Tyr113/His113 genotype or His113/His113 genotype (P = 0.01). In coke-oven workers, the subjects with the GSTP1 gene Val/Val genotype had significantly higher CBMN frequencies than those with the Ile/Ile (P = 0.05) and Ile/Val genotype (P = 0.01) with adjustment for urinary 1-OHP, age, sex, and cigarettes per day in the model of multivariate analysis of covariance. Whereas in non–coke-oven workers the Val allele of GSTP1 gene seemed to be associated with lower CBMN frequencies, the sample size for the subjects (n = 2) with the Val/Val genotype was too small to have a valid comparison. In coke-oven workers, the CBMN frequency was found to be lower in subjects with the GSTM1 non-null genotype than in those with GSTM1 null genotype, although the difference did not reach the significance level (P = 0.12). Based on the in vitro functional expression study of the variant alleles at residues 113 (exon 3, His113 slow allele) and 139 (exon 4, Arg139 rapid allele; refs. 44-46), three mEH enzymatic activity phenotypes (low, intermediate, and high) were assigned. Low activity phenotype group (LA phenotype) consisted of subjects homozygous for His139 and homozygous for His113 or heterozygous for His113, high activity phenotype group (HA phenotype) was homozygous for Tyr113 and homozygous for Arg139 or heterozygous for Arg139, and the subjects with remaining phenotypes were intermediate mEH activity phenotype group (IA phenotype). The coke-oven workers with LA phenotype of mEH had the lowest CBMN frequencies, whereas those with the HA phenotype had the highest CBMN frequencies, and the difference was statistically significant with adjustment for urinary 1-OHP, age, sex, and cigarettes per day in the model of multivariate analysis of covariance (P = 0.01; Table 5). The different effects of mEH phenotypes on CBMN frequencies in subjects with different occupational PAH exposure suggested the existence of gene-environment interaction between mEH phenotype and occupational PAH exposure. No other significant associations between CBMN frequencies and genetic polymorphisms of metabolic enzymes were found. The differences in CBMN frequencies between coke-oven workers and non–coke-oven workers in subgroups by genotypes or phenotypes remained significantly different.


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Table 3. CBMN frequency ({per thousand}) in coke-oven and non–coke-oven workers by genotypes of phase I metabolic enzymes

 

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Table 4. CBMN frequency ({per thousand}) in coke-oven and non–coke-oven workers by genotypes of phase II metabolic enzymes

 

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Table 5. CBMN frequency ({per thousand}) in coke-oven and non–coke-oven workers by phenotypes of mEH and NAT2

 
The joint effect between mEH phenotypes and GSTM1 genotypes on CBMN frequency is shown in Table 6. In coke-oven workers, the difference in CBMN frequencies between subjects with LA phenotype of mEH and GSTM1 non-null genotype (with the lowest CBMN frequency, 8.2 ± 7.1{per thousand}) and those with IA or HA phenotype of mEH and GSTM1 null genotype (with the highest CBMN frequency, 11.1 ± 6.1{per thousand}) was statistically significant (P = 0.02) with adjustment for urinary 1-OHP, age, sex, and cigarettes per day in the model of multivariate analysis of covariance; however, this joint effect between these two polymorphisms was not evident in non–coke-oven workers. The different effects of combined mEH and GSTM1 genotypes on CBMN frequencies in subjects with different occupational PAH exposure also suggested the existence of gene-environment interaction. The CBMN frequencies between coke-oven workers and non–coke-oven workers in subgroups by combined mEH and GSTM1 genotypes remained significantly different.


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Table 6. Joint effect of mEH phenotypes and GSTM1 genotypes on CBMN frequency ({per thousand}) in coke-oven and non–coke-oven workers

 

    Discussion
 Top
 Abstract
 Introduction
 Materials and Methods
 Results
 Discussion
 References
 
Accurate measurement of PAH exposure levels is important for evaluating PAH-induced early genetic and cytogenetic effects and investigating the modification effect or gene-environment interaction on PAH-induced adverse effects in coke-oven workers. In the present study, the coke-oven workers seemed to have been exposed to a high level of PAHs based on the stationery environmental monitoring, including air BSM and particulate-phase B(a)P, and high level of urinary 1-OHP. The PAH exposure of coke-oven workers in the present study was slightly higher than that in Zhang's study conducted in another steel company in China (13) and much higher than that reported by several other studies using CBMN assay (47-51).

In the present study, the associations between PAH exposure and increase of CBMN frequencies in coke-oven workers suggested that the CBMN assay could be used to detect the PAH-induced chromosomal damage in those who had been exposed to high levels of PAHs. The increase of CBMN frequencies with age, higher values of CBMN frequencies in women, and no effect of smoking and alcohol status on CBMN frequencies in coke-oven workers found in our study were consistent with the results of international collaborative projects aiming to assess the experimental protocol variations and the influence of age, sex, and lifestyle on CBMN frequencies (52-54). However, there were very few workers smoking 30+ cigarettes per day in our population, which exclude us to validate the effect of extreme smoking (30+ cigarettes per day) on CBMN frequencies (53). As the nonexposed controls were medical staff, it could be imagined that their socioeconomic status may differ from the coke-oven workers. However, the nonexposed controls worked in the hospital for occupational diseases affiliated to the steel company, so the average income and education degree of these medical staff were only slightly higher than those of coke-oven workers. At present, no direct evidence suggested that the socioeconomic status could influence CBMN frequencies. Therefore, the socioeconomic status may not be a critical factor influencing the relationship between coke-oven emission exposure and CBMN frequencies.

The distributions of CYP1A1, CYP2E1, GSTM1, GSTT1, GSTP1, mEH, NQO1, and NAT2 genotypes were similar in non–coke-oven workers and coke-oven workers and consistent with those described in the literature for the Chinese population (55, 56), which suggested no selection bias for the subjects' enrolment in terms of genotypes.

However, coke-oven workers with slow mEH genotype/phenotype had significantly lower CBMN frequencies than those coke-oven workers with high mEH genotype/phenotype with adjustment for other covariates, which was consistent with the reported findings that slow mEH genotype/phenotype was associated with lower levels of DNA adducts, urinary mutagenicity, and BPDE-serum albumin adducts (16, 26) and decreased lung cancer risk in heavy smokers (43). In an in vitro study using peripheral blood lymphocytes from 38 healthy donors, Salama et al. (46) found that the His113 allele (slow allele) of mEH was associated with significantly reduced frequency of B(a)P-induced chromosomal aberration and that the high mEH phenotype had significantly higher B(a)P-induced chromosomal aberration frequency than did all other genotypes. Although additional studies are still needed to provide a clear mechanistic explanation for our findings, it seemed that individuals with the His113 allele or low mEH activity phenotype had reduced ability to activate the trans-7,8-diol to the ultimate carcinogenic BPDE and hence had a low susceptibility to the genotoxic effects of PAHs.

The superfamily of glutathione S-transferase, mainly µ and {pi}, catalyzes transfer of reduced glutathione to PAH-derived epoxides, hydroxides, etc., and homozygous deletion of GSTM1 causes a loss of GSTM1 enzyme activity (57). In our study, the GSTM1 null genotype was associated with an increased CBMN frequencies in coke-oven workers, although the difference was not statistically significant (P = 0.12) but consistent with the findings in an in vitro study, in which the GSTM1 null genotype was found to be associated with a significantly (P < 0.02) increased frequency of chromosomal aberration induced by B(a)P (46). The GSTM1 null genotype had been found to be associated with increased levels of DNA adducts (15, 17, 19, 20, 22), BPDE-serum albumin levels (21), urinary mutagen excretion (25), and increased risk of lung cancer (58). These results combined with ours provided evidence to support the influence of GSTM1 genotypes on biological effects of exposure in occupationally PAH-exposed populations.

GSTP1 is another important glutathione S-transferase responsible for the metabolism of PAHs. In our study, the coke-oven workers homozygous for the GSTP1 Val104 allele had significantly higher CBMN frequencies than those with the Ile104 allele. This finding is also consistent with previous reports. The GSTP1 Val104 allele had been found to be associated with increased BPDE-DNA adducts in coke-oven workers (16) and increased urinary 8-hydroxydeoxyguanosine levels in pot-room workers (27). These findings combined with ours suggested that, when highly exposed to PAHs as seen in coke-oven workers, the subjects with the GSTP1 Val104/Val104 genotype may be more likely to be prone to genotoxicity than those without this genotype. Interestingly, in our study, the non–coke-oven workers homozygous for the GSTP1 Val104 allele had reduced CBMN frequencies. Because the sample size was too small for the GSTP1 Val104/Val104 genotype in non–coke-oven workers used as the reference group (n = 2), whether this finding was only a chance finding or of mechanistic significance needs to be validated in further studies with larger sample sizes.

CYP1A1 polymorphism is often considered to be associated with enhanced inducibility, leading to higher enzymatic activity that activates precarcinogens. The CYP1A1 variant genotype has been found to be associated with higher levels of DNA adducts in coke-oven workers (15, 17), increased tail inertias of single cell agarose electrophoresis in pot-room workers (27), and increased sister chromatid exchange frequencies in traffic policemen (28). Although we did not find any relationship between Ile/Val polymorphism in exon 7 of the CYP1A1 and CBMN frequency, we did observed that the PAH exposure level was higher in coke-oven workers (urinary 1-OHP, 12.0 µmol/mol creatinine) than in non–coke-oven workers (0.7 µmol/mol creatinine). In such a condition, the metabolic pathway of PAHs catalyzed by CYP1A1 may be saturated and the effect of the CYP1A1 polymorphism on the CBMN frequency may be insignificant. However, this speculation needs to be validated in larger studies.

We did not find any significant associations between GSTT1, NQO1, CYP2E1, and NAT2 polymorphisms and CBMN frequencies, which suggested that the formation of CBMN may not be related to the pathways catalyzed by these enzymes. Another possibility is that our study did not have the power to detect small differences in CBMN frequencies among or between genotypes of these metabolic genes in coke-oven workers exposed to high level of PAHs.

The joint effect between the high mEH phenotype and the GSTM1 null genotype on CBMN frequencies was also found, which suggested that subjects with high ability to transform trans-7,8-diol to ultimate carcinogenic BPDE and with low ability to detoxify PAHs would be at a greater risk for chromosomal damage when exposed to a high level of PAHs. In the present study, the gene-environment interactions between occupational PAH exposure and mEH phenotypes or combinations of mEH phenotypes and GSTM1 genotypes were also evident, which suggested that the gene-environment interactions between PAH exposure and polymorphism of certain metabolic genes were important mechanism for the PAH-induced chromosomal damage.

In conclusion, our findings indicate that polymorphisms in mEH, GSTP1, and GSTM1 may play significant roles in human sensitivity to the genotoxic effects of PAH exposure. However, our study had limitations due to a relatively small sample size that was not big enough to delineate the effect of rare polymorphisms, such as the GSTP1 Val104/Val104 genotype. Several important events involved in the CBMN formation (e.g., cell cycle control and DNA repair) were not a part of this study and should be investigated in further studies.


    Acknowledgments
 
We thank Dr. Qingyi Wei (Department of Epidemiology, University of Texas M.D. Anderson Cancer Center, Houston, TX) for his critical review, scientific editing, and comments on the article.


    Footnotes
 
Grant support: National Key Basic Research and Development Program (2002CB512903) and National Nature Science Foundation of China (39970633).

The costs of publication of this article were defrayed in part by the payment of page charges. This article must therefore be hereby marked advertisement in accordance with 18 U.S.C. Section 1734 solely to indicate this fact.

Received 1/20/04; revised 4/29/04; accepted 5/10/04.


    References
 Top
 Abstract
 Introduction
 Materials and Methods
 Results
 Discussion
 References
 

  1. IARC. Monographs on the evaluation of the carcinogenic risk of chemicals to humans. Vol. 32. Polycyclic aromatic hydrocarbons. Part 1. Chemical, environmental and experimental data. France: IARC; 1983.
  2. IARC. Monographs on the evaluation of the carcinogenic risk of chemicals to humans. Vol. 34. Polycyclic aromatic hydrocarbons. Part 3. Industrial exposure in aluminum production, coal gasification, coke production, and iron and steel founding. France: IARC; 1984.
  3. IARC. Monographs on the evaluation of the carcinogenic risk of chemicals to humans. Suppl. 7. France: IARC; 1987.
  4. Jongeneelen FJ, Benchmark guideline for urinary 1-hydroxypyrene as biomarker of occupational exposure to polycyclic aromatic hydrocarbons. Ann Occup Hyg 2001;45:3–13.[Abstract/Free Full Text]
  5. Miller EC, Miller JA. Mechanisms of chemical carcinogenesis. Cancer 1981;47:1055–64.
  6. International Programme on Chemical Safety. Environmental Health Criteria 202: selected non-heterocyclic polycyclic aromatic hydrocarbons. Geneva: WHO; 1998.
  7. Daly AK, Cholerton S, Gregory W, Idle JR. Metabolic polymorphisms. Pharmacol Ther 1993;57:129–60.[CrossRef][Medline]
  8. Joseph P, Jaiswal AK. NAD(P)H:quinone oxidoreductase1 (DT diaphorase) specifically prevents the formation of benzo[a]pyrene quinone-DNA adducts generated by cytochrome P4501A1 and P450 reductase. Proc Natl Acad Sci U S A 1994;91:8413–7.[Abstract/Free Full Text]
  9. Smith CA, Smith G, Wolf CR. Genetic polymorphisms in xenobiotic metabolism. Eur J Cancer 1994;30:1921–35.
  10. Fenech M. The cytokinesis-block micronucleus technique: a detailed description of the method and its application to genotoxicity studies in human populations. Mutat Res 1993;285:35–44.[Medline]
  11. Fenech M. The in vitro micronucleus technique. Mutat Res 2000;455:81–95.[Medline]
  12. Fenech M. Chromosomal biomarkers of genomic instability relevant to cancer. Drug Discov Today 2002;7:1128–37.[CrossRef][Medline]
  13. Fenech M. Biomarkers of genetic damage for cancer epidemiology. Toxicology 2002;181–182:411–6.
  14. Zhang J, Ichiba M, Hara K, et al. Urinary 1-hydroxypyrene in coke oven workers relative to exposure, alcohol consumption, and metabolic enzymes. Occup Environ Med 2001;58:716–21.[Abstract/Free Full Text]
  15. Rojas M, Cascorbi I, Alexandrov K, et al. Modulation of benzo[a]pyrene diolepoxide-DNA adduct levels in human white blood cells by CYP1A1, GSTM1 and GSTT1 polymorphism. Carcinogenesis 2000;21:35–41.[Abstract/Free Full Text]
  16. Kuljukka-Rabb T, Nylund L, Vaaranrinta R, et al. The effect of relevant genotypes on PAH exposure-related biomarkers. J Expo Anal Environ Epidemiol 2002;12:81–91.[CrossRef][Medline]
  17. Brescia G, Celotti L, Clonfero E, et al. The influence of cytochrome P450 1A1 and glutathione S-transferase M1 genotypes on biomarker levels in coke-oven workers. Arch Toxicol 1999;73:431–9.[CrossRef][Medline]
  18. Van Delft JH, Steenwinkel MS, van Asten JG, et al. Biological monitoring the exposure to polycyclic aromatic hydrocarbons of coke oven workers in relation to smoking and genetic polymorphisms for GSTM1 and GSTT1. Ann Occup Hyg 2001;45:395–408.[Abstract/Free Full Text]
  19. Viezzer C, Norppa H, Clonfero E, et al. Influence of GSTM1, GSTT1, GSTP1, and EPHX gene polymorphisms on DNA adduct level and HPRT mutant frequency in coke-oven workers. Mutat Res 1999;431:259–69.[Medline]
  20. Pavanello S, Gabbani G, Mastrangelo G, Brugnone F, Maccacaro G, Clonfero E. Influence of GSTM1 genotypes on anti-BPDE-DNA adduct levels in mononuclear white blood cells of humans exposed to PAH. Int Arch Occup Environ Health 1999;72:238–46.[CrossRef][Medline]
  21. Pastorelli R, Cerri A, Rozio M, et al. Benzo(a)pyrene diolepoxide adducts to albumin in workers exposed to polycyclic aromatic hydrocarbons: association with specific CYP1A1, GSTM1, GSTP1 and EHPX genotypes. Biomarkers 2001;6:357–74.[CrossRef]
  22. Tuominen R, Baranczewski P, Warholm M, Hagmar L, Moller L, Rannug A. Susceptibility factors and DNA adducts in peripheral blood mononuclear cells of aluminum smelter workers exposed to polycyclic aromatic hydrocarbons. Arch Toxicol 2002;76:178–86.[CrossRef][Medline]
  23. Carstensen U, Alexandrie AK, Hogstedt B, Rannug A, Bratt I, Hagmar L. B- and T-lymphocyte micronuclei in chimney sweeps with respect to genetic polymorphism for CYP1A1 and GST1 (class µ). Mutat Res 1993;289:187–95.[CrossRef][Medline]
  24. Nielsen PS, de Pater N, Okkels H, Autrup H. Environmental air pollution and DNA adducts in Copenhagen bus drivers-effect of GSTM1 and NAT2 genotypes on adduct levels. Carcinogenesis 1996;17:1021–7.[Abstract/Free Full Text]
  25. Gabbani G, Pavanello S, Nardini B, et al. Influence of metabolic genotype GSTM1 on levels of urinary mutagens in patients treated topically with coal tar. Mutat Res 1999;440:27–33.[Medline]
  26. Pastorelli R, Guanci M, Cerri A, et al. Impact of inherited polymorphisms in glutathione S-transferase M1, microsomal epoxide hydrolase, cytochrome P450 enzymes on DNA, and blood protein adducts of benzo(a)pyrene-diolepoxide. Cancer Epidemiol Biomarkers Prev 1998;7:703–9.[Abstract]
  27. Carstensen U, Hou SM, Alexandrie AK, et al. Influence of genetic polymorphisms of biotransformation enzymes on gene mutations, strand breaks of deoxyribonucleic acid, and micronuclei in mononuclear blood cells and urinary 8-hydroxydeoxyguanosine in potroom workers exposed to polyaromatic hydrocarbons. Scand J Work Environ Health 1999;25:351–60.[Medline]
  28. Carere A, Andreoli C, Galati R, et al. Biomonitoring of exposure to urban air pollutants: analysis of sister chromatid exchanges and DNA lesions in peripheral lymphocytes of traffic policemen. Mutat Res 2002;518:215–24.[Medline]
  29. Organic Methods Evaluation Branch, OSHA Analytical Laboratory. Coal tar pitch volatiles (CTPVs), coke oven emissions (COE), and selected polynuclear aromatic hydrocarbons (PAH). OSHA Method 58. Salt Lake City (UT): OSHA; 1986.
  30. Jongeneelen FJ, Bos RP, Anzion RB, Theuws JL, Henderson PT. Biological monitoring of polycyclic aromatic hydrocarbons. Metabolites in urine. Scand J Work Environ Health 1986;12:137–43.[Medline]
  31. Li XH, Leng SG, Guo J, Guan L, Zheng YX. An improved high performance liquid chromatography method for determination of 1-hydroxypyrene in urine [in Chinese]. J Hyg Res 2003;32:616–7.
  32. Hornung RW, Reed LD. Estimation of average concentration in the presence of nondetectable values. Appl Occup Environ Hyg 1990;5:46–51.
  33. Fenech M, Chang WP, Kirsch-Volders M, Holland N, Bonassi S, Zeiger, E. Human MicroNucleus project. HUMN project: detailed description of the scoring criteria for the cytokinesis-block micronucleus assay using isolated human lymphocyte cultures. Mutat Res 2003;534:65–75.[Medline]
  34. Miller SA, Dykes DD, Polesky HF. A simple salting out procedure for extracting DNA from human nucleated cells. Nucleic Acids Res 1988;16:1215.[Free Full Text]
  35. Hayashi SI, Watanabe J, Nakachi K, Kawajiri K. PCR detection of an A/G polymorphism within exon 7 of the CYP1A1 gene. Nucleic Acids Res 1991;19:4797.[Free Full Text]
  36. Stephens EA, Taylor JA, Kaplan N, et al. Ethnic variation in the CYP2E1 gene: polymorphism analysis of 695 African-Americans, European-Americans and Taiwanese. Pharmacogenetics 1994;4:185–92.[Medline]
  37. Kato S, Shields PG, Caporaso NE, et al. Cytochrome P450IIE1 genetic polymorphisms, racial variation, and lung cancer risk. Cancer Res 1992;52:6712–5.[Abstract/Free Full Text]
  38. Saarikoski ST, Voho A, Reinikainen M, et al. Combined effect of polymorphic GST genes on individual susceptibility to lung cancer. Int J Cancer 1998;77:516–21.[CrossRef][Medline]
  39. Chan P, Monte DD, Jiang XQ. Identification of an NAD(P)H:quinine oxidoreductase polymorphism and its association with Parkinson's disease. Mov Disord 1997;12:26.
  40. Zhong S, Wyllie AH, Barnes D, Wolf CR, Spurr NK. Relationship between the GSTM1 genetic polymorphism and susceptibility to bladder, breast and colon cancer. Carcinogenesis 1993;14:1821–4.[Abstract/Free Full Text]
  41. Katoh T, Nagata N, Kuroda Y, et al. Glutathione S-transferase M1 (GSTM1) and T1 (GSTT1) genetic polymorphism and susceptibility to gastric and colorectal adenocarcinoma. Carcinogenesis 1996;17:1855–9.[Abstract/Free Full Text]
  42. Hickman D, Sim E. N-acetyltransferase polymorphism. Comparison of phenotype and genotype in humans. Biochem Pharmacol 1991;42:1007–14.[CrossRef][Medline]
  43. Zhou W, Thurston SW, Liu G, et al. The interaction between microsomal epoxide hydrolase polymorphisms and cumulative cigarette smoking in different histological subtypes of lung cancer. Cancer Epidemiol Biomarkers Prev 2001;10:461–6.[Abstract/Free Full Text]
  44. Hassett C, Aicher L, Sidhu JS, Omiecinski CJ. Human microsomal epoxide hydrolase: genetic polymorphism and functional expression in vitro of amino acid variants. Hum Mol Genet 1994;3:421–8. Erratum in: Hum Mol Genet 1994;3:1214.[Abstract/Free Full Text]
  45. Hassett C, Lin J, Carty CL, Laurenzana EM, Omiecinski CJ. Human hepatic microsomal epoxide hydrolase: comparative analysis of polymorphic expression. Arch Biochem Biophys 1997;337:275–83.[CrossRef][Medline]
  46. Salama SA, Sierra-Torres CH, Oh HY, Hamada FA, Au WW. Variant metabolizing gene alleles determine the genotoxicity of benzo[a]pyrene. Environ Mol Mutagen 2001;37:17–26.[CrossRef][Medline]
  47. Forni A, Guanti G, Bukvic N, Ferri G, Foa V. Cytogenetic studies in coke oven workers. Toxicol Lett 1996;88:185–9.[CrossRef][Medline]
  48. Buchet JP, Ferreira MJ, Burrion JB, et al. Tumor markers in serum, polyamines and modified nucleosides in urine, and cytogenetic aberrations in lymphocytes of workers exposed to polycyclic aromatic hydrocarbons. Am J Ind Med 1995;27:523–43.[Medline]
  49. Van Hummelen P, Gennart JP, Buchet JP, Lauwerys R, Kirsch-Volders M. Biological markers in PAH exposed workers and controls. Mutat Res 1993;300:231–9.[CrossRef][Medline]
  50. Leopardi P, Zijno A, Marcon F, et al. Analysis of micronuclei in peripheral blood lymphocytes of traffic wardens: effects of exposure, metabolic genotypes, and inhibition of excision repair in vitro by ARA-C. Environ Mol Mutagen 2003;41:126–30.[CrossRef][Medline]
  51. Bolognesi C, Merlo F, Rabboni R, Valerio F, Abbondandolo A. Cytogenetic biomonitoring in traffic police workers: micronucleus test in peripheral blood lymphocytes. Environ Mol Mutagen 1997;30:396–402.[CrossRef][Medline]
  52. Bonassi S, Fenech M, Lando C, et al. Human MicroNucleus project: international database comparison for results with the cytokinesis-block micronucleus assay in human lymphocytes. I. Effect of laboratory protocol, scoring criteria, and host factors on the frequency of micronuclei. Environ Mol Mutagen 2001;37:31–45.[CrossRef][Medline]
  53. Bonassi S, Neri M, Lando C, et al. HUMN collaborative group. Effect of smoking habit on the frequency of micronuclei in human lymphocytes: results from the Human MicroNucleus project. Mutat Res 2003;543:155–66.[CrossRef][Medline]
  54. Bolognesi C, Lando C, Forni A, et al. Chromosomal damage and aging: effect on micronuclei frequency in peripheral blood lymphocytes. Age Ageing 1999;28:393–7.[Abstract/Free Full Text]
  55. Yin L, Pu Y, Liu TY, Tung YH, Chen KW, Lin P. Genetic polymorphisms of NAD(P)H quinone oxidoreductase, CYP1A1 and microsomal epoxide hydrolase and lung cancer risk in Nanjing, China. Lung Cancer 2001;33:133–41.[CrossRef][Medline]
  56. Leng S, Song W, Wang Y, Liu Y, Zheng Y. The genetic polymorphisms of three kinds of glutathione S-transferases in Chinese Han population [in Chinese]. Zhonghua Yu Fang Yi Xue Za Zhi 2001;35:159–62.
  57. Seidegard J, Vorachek WR, Pero RW, Pearson WR, Hereditary differences in the expression of the human glutathione transferase active on trans-stilbene oxide are due to a gene deletion. Proc Natl Acad Sci U S A 1988;85:7293–7.[Abstract/Free Full Text]
  58. Lan Q, He X, Costa DJ, et al. Indoor coal combustion emissions, GSTM1 and GSTT1 genotypes, and lung cancer risk: a case-control study in Xuan Wei, China. Cancer Epidemiol Biomarkers Prev 2000;9:605–8.[Abstract/Free Full Text]



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