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Genetic Polymorphisms in XRCC1, CD3EAP, PPP1R13L, XPB, XPC, and XPF and the Risk of Chronic Benzene Poisoning in a Chinese Occupational Population

  • Ping Xue ,

    Contributed equally to this work with: Ping Xue, Lin Gao

    Affiliation Department of Toxicology, School of Public Health, China Medical University, Shenyang, Liaoning, P.R. China

  • Lin Gao ,

    Contributed equally to this work with: Ping Xue, Lin Gao

    Affiliations Department of Toxicology, School of Public Health, China Medical University, Shenyang, Liaoning, P.R. China, Poisoning Department, Shenyang ninth people’s Hospital, Shenyang, Liaoning, P.R. China

  • Sha Xiao,

    Affiliation Department of Toxicology, School of Public Health, China Medical University, Shenyang, Liaoning, P.R. China

  • Guopei Zhang,

    Affiliation Department of Toxicology, School of Public Health, China Medical University, Shenyang, Liaoning, P.R. China

  • Mingyang Xiao,

    Affiliation Department of Toxicology, School of Public Health, China Medical University, Shenyang, Liaoning, P.R. China

  • Qianye Zhang,

    Affiliation Department of Toxicology, School of Public Health, China Medical University, Shenyang, Liaoning, P.R. China

  • Xiao Zheng,

    Affiliation Department of Toxicology, School of Public Health, China Medical University, Shenyang, Liaoning, P.R. China

  • Yuan Cai,

    Affiliation Department of Toxicology, School of Public Health, China Medical University, Shenyang, Liaoning, P.R. China

  • Cuihong Jin,

    Affiliation Department of Toxicology, School of Public Health, China Medical University, Shenyang, Liaoning, P.R. China

  • Jinghua Yang,

    Affiliation Department of Toxicology, School of Public Health, China Medical University, Shenyang, Liaoning, P.R. China

  • Shengwen Wu,

    Affiliation Department of Toxicology, School of Public Health, China Medical University, Shenyang, Liaoning, P.R. China

  • Xiaobo Lu

    Affiliation Department of Toxicology, School of Public Health, China Medical University, Shenyang, Liaoning, P.R. China

Genetic Polymorphisms in XRCC1, CD3EAP, PPP1R13L, XPB, XPC, and XPF and the Risk of Chronic Benzene Poisoning in a Chinese Occupational Population

  • Ping Xue, 
  • Lin Gao, 
  • Sha Xiao, 
  • Guopei Zhang, 
  • Mingyang Xiao, 
  • Qianye Zhang, 
  • Xiao Zheng, 
  • Yuan Cai, 
  • Cuihong Jin, 
  • Jinghua Yang



Individual variations in the capacity of DNA repair machinery to relieve benzene-induced DNA damage may be the key to developing chronic benzene poisoning (CBP), an increasingly prevalent occupational disease in China. ERCC1 (Excision repair cross complementation group 1) is located on chromosome 19q13.2–3 and participates in the crucial steps of Nucleotide Excision Repair (NER); moreover, we determined that one of its polymorphisms, ERCC1 rs11615, is a biomarker for CBP susceptibility in our previous report. Our aim is to further explore the deeper association between some genetic variations related to ERCC1 polymorphisms and CBP risk.


Nine single nucleotide polymorphisms (SNPs) of XRCC1 (X-ray repair cross-complementing 1), CD3EAP (CD3e molecule, epsilon associated protein), PPP1R13L (protein phosphatase 1, regulatory subunit 13 like), XPB (Xeroderma pigmentosum group B), XPC (Xeroderma pigmentosum group C) and XPF (Xeroderma pigmentosum group F) were genotyped by the Snapshot and TaqMan-MGB® probe techniques, in a study involving 102 CBP patients and 204 controls. The potential interactions between these SNPs and lifestyle factors, such as smoking and drinking, were assessed using a stratified analysis.


An XRCC1 allele, rs25487, was related to a higher risk of CBP (P<0.001) even after stratifying for potential confounders. Carriers of the TT genotype of XRCC1 rs1799782 who were alcohol drinkers (OR = 8.000; 95% CI: 1.316–48.645; P = 0.022), male (OR = 9.333; 95% CI: 1.593–54.672; P = 0.019), and had an exposure of ≤12 years (OR = 2.612; 95% CI: 1.048–6.510; P = 0.035) had an increased risk of CBP. However, the T allele in PPP1R13L rs1005165 (P<0.05) and the GA allele in CD3EAP rs967591 (OR = 0.162; 95% CI: 0039~0.666; P = 0.037) decreased the risk of CBP in men. The haplotype analysis of XRCC1 indicated that XRCC1 rs25487A, rs25489G and rs1799782T (OR = 15.469; 95% CI: 5.536–43.225; P<0.001) were associated with a high risk of CBP.


The findings showed that the rs25487 and rs1799782 polymorphisms of XRCC1 may contribute to an individual’s susceptibility to CBP and may be used as valid biomarkers. Overall, the genes on chromosome 19q13.2–3 may have a special significance in the development of CBP in occupationally exposed Chinese populations.


Benzene, a commonly used industrial chemical, is an established human carcinogen [1]. It has been documented that long-term occupational exposure to benzene may induce chronic benzene poisoning (CBP), which could act on the bone marrow and peripheral blood cells and cause leukemia or other hematopoietic cancers in humans [2,3]. However, the susceptibility to benzene toxicity varies among individuals after a similar occupational exposure [4]. This suggests that in addition to environmental exposure, genetic polymorphisms render some individuals more susceptible to CBP. Therefore, it is critical to identify valid biomarkers in the susceptible population after occupational benzene exposure and to predict the risk of developing CBP before the disease occurs.

Benzene produces adverse effects through its metabolites, quinones and reactive oxygen species (ROS) [57]. Benzene’s reactive intermediates can form DNA adducts by covalently binding to macromolecules, including DNA and proteins, and ultimately give rise to single- or double-strand DNA damage [8]. The genetic damage induced by occupational exposure to benzene could directly cause oxidative damage and covalent DNA adducts [9]. Thus, a properly functioning DNA repair process is required to maintain genomic stability and prevent the mutated cells from subsequently developing into malignancies [10]. Normally, the DNA damage caused by the benzene metabolites could initiate the cellular DNA repair system. Variations in DNA repair genes may result in an individual’s susceptibility to CBP. Benzene-induced DNA damage would primarily be repaired by the NER and BER systems. BER is responsible for repairing chemically induced DNA damage at a single base, including the removal of oxidative damage and single-strand breaks. NER is involved in the restoration of a wide variety of DNA damage and structural distortions to the DNA double helix, including the large benzene-induced DNA adducts. XRCC1 (X-ray repair cross-complementing 1) acts as an indispensable factor in BER, and a clear relationship between its polymorphisms and chronic benzene poisoning has been identified. Cooperating with ADPRT (ADP ribosyltransferase), DNA polymerase β and DNA ligase III, XRCC1 could repair the gaps left acts as a scaffold after the excision of benzene DNA adducts (p-benzoquinone)[1115]. As shown in our previous studies, a SNP at codon 118 (rs11615) of ERCC1 (Excision repair cross complementation group 1), a key element in the NER system, could modify an individual’s risk of developing CBP. We hypothesized that genetic polymorphism in other NER genes, such as XPB (Xeroderma pigmentosum group B), XPC (Xeroderma pigmentosum group C) and XPF (Xeroderma pigmentosum group F), which have not been studied, may be related to an individual’s susceptibility to benzene toxicity.

Interestingly, both XRCC1 and ERCC1 are located on chromosome 19q13.2–3, an active zone involved in DNA repair, apoptosis, and cell proliferation. PPP1R13L (protein phosphatase 1, regulatory subunit 13 like) and CD3EAP (CD3e molecule, epsilon-associated protein) are also located in this region and situated between ERCC1 and ERCC2. Previous studies have demonstrated a relationship between the risk of developing cancer and polymorphisms located in this region [1619]. Moreover, it was reported that the overlapping genes ERCC1, CD3EAP, and PPP1R13L may interact in apoptosis and DNA repair pathways [16, 17, 20, 21]. PPP1R13L is an inhibitor of p53 that primarily affects apoptosis [22]. CD3EAP encodes a nucleoprotein that is localized to the fibrillar centers of the nucleolus and may be a member of the RNA polymerase I transcription complex. In addition, CD3EAP is positioned in an anti-sense orientation to and overlaps with ERCC1. This exceptional type of gene overlap is conserved in the mouse, suggesting that this chromosomal structure has an important biological function [23].

After comprehensively considering these points, we conducted a case-control study to further explore the potential relationship between the polymorphisms of the genes located on 19q13.2–3 or those that are involved in NER and the risk of CBP in a Chinese occupational population. Finally, we identified some valid biomarkers to predict the risk of CBP, which may help protect the health of the population that is occupationally exposed to benzene.

Materials and Methods

Study subjects

The study population has previously been exhaustively described [24]. In brief, we recruited 102 CBP patients from several major factories in Shenyang, China as our cases. Benzene poisoning was diagnosed from 1986 to 2011 by the local authorized Occupational Disease Diagnostic Team, China, and includes (a) total WBC counts <4000/μl or WBC counts between 4000 and 4500/μl and platelet counts <80,000/μl, with repeated confirmation of these counts after a few months in a peripheral blood examination; (b) documented benzene exposure as a result of employment in the factory for at least 6 months; and (c) the exclusion of other known causes of abnormal blood counts, such as chloromycetin use and ionizing radiation. The medical records of these patients were independently reviewed by at least two hemopathologists, particularly those with WBC counts >3500 to confirm the CBP diagnosis. Of the 112 eligible patients, 102 (90%) agreed to participate in this study. The diagnostic criteria for occupational CBP are provided by the Ministry of Health, China. Two hundred four healthy workers from the same factories who had been occupationally exposed to similar amounts of benzene in the work environment as the cases were selected as the controls. The cases and controls were matched for age, sex and exposure duration. Each participant donated 2 ml of venous blood and their demographic data were recorded. The intensity of benzene exposure (milligrams per cubic meter) for the patients was used as the benzene exposure level in the workplace while the patients were being diagnosed; the intensity of benzene exposure for the controls was used as the current level and monitored by organic vapor passive dosimetry badges during the collection of the blood samples. The subjects were administered a rigorous physical examination in the Shenyang Occupational Disease Hospital.

Ethics Statement

The protocol and consent form were approved by the Institutional Review Board of China Medical University prior to the study. Informed consent was obtained from each of the participants after a detailed explanation of the nature and possible consequences of the study. Each participant donated 2 ml venous blood only after written informed consent was obtained and their demographic data (ethnic background, smoking status, alcohol consumption, protective measures, medical history and occupational history, such as work unit, type of work and exposure duration) were recorded in detailed questionnaires. All activities involving human subjects were performed under full compliance with the government’s policies and the Declaration of Helsinki.

DNA preparation

Venous blood (2 ml) was drawn from each subject and collected with a folic acid sodium anti-coagulant. The subjects’ DNA was routinely extracted from these samples by phenol chloroform extraction, which has been described elsewhere.

SNaPshot analysis

In our experiments, XPB (rs4150441, G>A), XPC (rs2228001, A>C and rs2279017, C>A), XPF (rs4781560, T>C), XRCC1 (rs25489, G>A) and PPP1R13L (rs1005165, C>T) were detected by multiplex PCR amplification and the probe primer extension SNaPshot reaction method according to the professional recommendation of Invitrogen Company. The procedure is described below.

Primer design.

Forward and reverse primers used in the multiplex PCR reaction and SNaPshot primers used as probes designed for the study are provided in Table 1 and Table 2. All primers for the reactions were designed using Primer 5 software.

Table 2. Probe primer sequences used for the SNaPshot extension reaction.

PCR amplification.

Multiplex PCR amplification was performed from 50 ng of genomic DNA in a final volume of 25 μl containing 2.5 μl of 10×PCR buffer, 0.8 μl of 50 mM MgCl2, 0.5 μl of 10 mM dNTP, 0.2 μl of Platinum® Taq DNA-polymerase, and 1 μl of a 5 μM stock of each primer. The PCR cycling conditions were 1 cycle of 94°C for 5 minutes; 33 cycles of 94°C for 30 seconds, 56°C for 30 seconds, and 72°C for 30 seconds; and 1 cycle of 72°C for 5 minutes. The multiplex PCR amplicons were analyzed on 3% (w/v) agarose gels before being treated with an Exo/SAP master mix containing 20 U/μl of Exonuclease-I (Fermentas) and 1 U/μl of Shrimp Alkaline Phosphatase (Fermentas) to remove the unincorporated primers and dNTPs (Invitrogen). The PCR product (2 μl) was incubated with 0.5 μl of the Exo/SAP master mix for 1 hour at 37°C followed by 15 minutes at 75°C to inactivate the enzyme. The second step consisted of a multiplex single-base primer extension reaction according to the manufacturer’s protocol. The final reaction volume was 3 μl containing 1 μl of the treated first-step PCR reaction, 1.5 μl of the SNaPshot ready reaction premix containing fluorescent dideoxy nucleotides (A = dR6G, green; C = dTAMRA, black; G = dR110, blue; T = dROX, red), and 0.5 μl of the probe primers. The reaction was performed under stringent conditions (25 cycles of 96°C for 10 seconds, 51°C for 5 seconds, and 60°C for 30 seconds). An aliquot of the SNaPshot extension reaction (5 μl) was then treated with 0.3 μl 1U/μl of SAP for 1 hour at 37°C followed by 15 minutes at 75°C to inactivate the enzyme before the third step of capillary electrophoresis.

Capillary electrophoresis.

The fluorescence and size of the extended products were determined by capillary electrophoresis on a 3730 genetic analyzer (Applied Biosystem) using a POP-7 polymer. Before being loaded onto the genetic analyzer, an aliquot of the treated SNaPshot multiplex extension reaction (1 μl) was mixed with 8.8 μl of Hidi-formamide (Applied Biosystems) and 0.2 μl of the size standard (GeneScan-120 LIZ ladder, Applied Biosystem). The data were analyzed using GeneMapper v4.0 and specific parameters.

TaqMan-MGB analysis

XRCC1 (rs25487, A>G, assay ID is C_622564_10, part number is 4351379; rs1799782, C>T, assay ID is C_11463404_10, part number is 4351379) and CD3EAP (rs967591, G>A, assay ID is C_8713992_1, part number is 4351379) were analyzed by TaqMan® sequencing on an ABI 7500 Real-time PCR system (ABI, US, Stagapore). All PCR reagents were purchased from ABI Company.

PCR amplification.

The PCR reactions were performed in a 20 μl reaction mixture: 10.0 μl of Premix Ex TaqTM, 0.4 μl of each probe and primer, and 2 μl of DNA (l0 ng/μl). The PCR reaction included an initial step at 95°C for 10 min, denaturation at 95°C for 5 s and extension at 60°C for 34 s.

Allelic discrimination plate read and analysis.

After PCR amplification, an endpoint plate read was performed using an Applied Biosystems Real-Time PCR System. The Sequence Detection System (SDS) Software uses the fluorescence measurements made during the plate read to plot the fluorescence (Rn) values based on the signals from each well. The plotted fluorescence signals indicate the alleles that are present in each sample.

Statistical analysis

All statistical analyses were performed with SPSS 19.0. To ensure a good fit to the Hardy-Weinberg equilibrium, the linkage disequilibrium (LD) for each SNP was tested using the Haploview Software (version 4.1, Broad Institute). A Fisher’s exact test or Chi-squared (χ2) test was selected to compare the frequencies of the different genetic polymorphisms between the cases and controls. The χ2 test was also used to evaluate the association between genetic polymorphisms and the risk of CBP. The analyses for the homogeneity of the odds ratios (OR) were performed using the Breslow–Day method. The OR and 95% confidence interval (95% CI) obtained from the multinomial logistic regression were used to analyze the association of the genetic polymorphisms with CBP after adjusting for potential confounders, including cigarette smoking, alcohol consumption, gender and the duration of benzene exposure. The frequency distribution of the haployptes was calculated by χ2 analysis. A two-tailed P-value < 0.05 was considered statistically significant.


Demographics of the cases and controls

A summary of selected characteristics of the subjects is shown in our previous publication [24]. In brief, the 102 CPB patients used as cases were characterized by a median age of 37.5 (range: 18.0–63.0) and an exposure duration of 10.0 (range: 2.0–32.0), and the 204 healthy people used as controls were characterized by a median age of 36.0 (range: 23.0–62.0) and an exposure duration of 10.0 (range: 1.0–35.0). More female participants than male participants (79.41% and 20.59%, respectively) were involved in this survey. A higher proportion of the cases were smokers than the controls (12.75% vs. 5.39%, P = 0.024), and the distribution of the other factors between the cases and controls were not significantly different.

Genetic polymorphisms of XRCC1, PPP1R13L, CD3EAP, XPB, XPC and XPF

The frequencies of the XRCC1, PPP1R13L, CD3EAP, XPB, XPC and XPF genotypes in the cases and controls are presented in Table 3. For XRCC1 rs25487, the allele distribution was significantly different between the cases and controls (P <0.01). In contrast, there were no differences in the other SNPs (P>0.05).

Table 3. Association between single nucleotide polymorphisms of PPP1R13L, XRCC1, XPC, XPF, XPB/ERCC3 and CD3EAP and the risk of CBP.

The effect of genetic polymorphisms on the risk of CBP were modified by the subjects’ lifestyles

A higher proportion of the cases carry the XRCC1 rs25487 AA genotype than the controls (49.50% vs. 15.84%, respectively) and the risk of CBP was correspondingly increased (OR = 14.063; 95% CI: 6.545–30.214; P < 0.001) compared to individuals carrying the GG genotype. The XRCC1 rs25487 AA genotype also seemed to be related to a higher risk of CBP after stratifying by smoking, alcohol consumption, gender and exposure duration (ORadj = 14.898; 95% CI: 6.781–32.732; P < 0.001) (Tables 37). The proportion of the XRCC1 rs1799782 TT genotype was higher in the cases than in the controls (16.67% vs. 8.46%, respectively) (Table 3). Subjects carrying the rs1799782 TT genotype had a higher risk of CBP (OR = 2.333; 95% CI: 1.014–4.930; P = 0.024) and the relationship was confined to alcohol drinkers (OR = 8.000; 95% CI: 1.316–48.645; P = 0.022), males (OR = 9.333; 95% CI: 1.593–54.672; P = 0.019), and an exposure duration of less than 12 years (OR = 2.612; 95% CI: 1.048–6.510; P = 0.035). Moreover, a clear relationship still existed for exposure duration after adjustment (Tables 5, 6 and 7). There was a high risk of CBP for individuals carrying the XPB rs4150441 GA genotype (OR = 1.729; 95% CI: 1.000–2.992; P = 0.049) and the GA+AA genotypes (OR = 1.716; 95% CI: 1.015–2.900; P = 0.043) compared to those carrying the GG genotype. However, the PPP1R13L rs1005165 T allele (CT genotype, TT genotype and CT+TT genotypes) and CD3EAP rs967591 GA and GA+AA genotypes exhibited a protective role against CBP development in males (P<0.05) (Table 6). There was no association between the risk of CBP and XPC and XPF polymorphisms in the present study (P > 0.05).

Table 4. The relationship between the single nucleotide polymorphisms and the risk of CBP, stratified by smoking status.

Table 5. The relationship between the single nucleotide polymorphisms and the risk of CBP, stratified by alcohol consumption.

Table 6. The relationship between the single nucleotide polymorphisms and the risk of CBP, stratified by gender.

Table 7. The relationship between the single nucleotide polymorphisms and the risk of CBP, stratified by exposure duration.

Effects of the Haplotypes on Risk of CBP

Using the Haploview 4.1 program and criteria based on the 95% confidence interval bounds on the D’ values, we performed a combined analysis of 10 SNPs encompassing XRCC1, XPC, XPF, PPP1R13L, CD3EAP and ERCC1; the genotyping data for ERCC1 that was used in the haplotype analysis were from our previous publication [24]. Three haplotype blocks with strong LD in the studied sub-region were identified and the results were presented in Table 8. The association between the haplotypes and CBP risk was assessed for each haplotype block and evaluated by χ2 analysis. There were statistically significant differences for the distribution of the XRCC1 rs25487A, rs25489G and rs1799782T haplotypes. Compared to those carrying the XRCC1 rs25487G, rs25489G and rs1799782C haplotypes, there was an increased risk of CBP with the AGT haplotypes (OR = 15.469, 95% CI: 5.536–43.225, P<0.001). In addition, the PPP1R13L, CD3EAP and ERCC1 polymorphisms are in linkage disequilibrium with each other in cancers, and XPC rs2228001 and rs2279017 and XPF rs4781560, which are located in the same region, had significant linkage disequilibrium. However, in the current study, there were no significant associations between these haplotypes and the risk of CBP.


It is well known that a valid DNA repair process after exposure to benzene and its metabolites may contribute to reduce the risk of chronic benzene poisoning (CBP). Mounting scientific evidence has shown that occupational exposure to benzene induces genetic damage, mainly due to chromosomal aberrations, disordered DNA structure and oxidative damage [2527]. Although some epidemiological studies on the association between the risk of CBP and polymorphism in DNA repair genes have been performed, the conclusions are controversial.

XRCC1, a central scaffolding protein involved in BER, is thought to be a critical element of an individual’s susceptibility to benzene genotoxicity [28]. Three coding polymorphisms, which are precisely located on these interacting domains, are identified in the XRCC1 gene, including rs25487 G>A (Arg→Gln), rs25489 G>A (Arg→His) and rs1799782 C>T (Arg→Trp) [29]. We hypothesized that these variations may affect the normal function of XRCC1 to repair benzene-induced DNA damage. We found that two XRCC1 SNPs (rs25487 and rs1799782) showed a close correlation with a higher risk of CBP. Recently, the significance of these two polymorphisms has been extensively emphasized in several cancers. The XRCC1 rs1799782 TT genotype was found to be associated with an increased risk of lung [30], esophageal [31], and cervical cancer [32] in a Chinese population, and the rs25487 AA genotype was linked to an increased risk of breast cancer among women [33] and pancreatic cancer [34] in a Chinese population. These two SNPs are also reported to be linked to the repair of benzene-induced DNA damage. A study of Thai laboratory workers who were occupationally exposed to benzene indicated that the participants carrying the XRCC1 rs25487 AA or GA genotypes had a reduced DNA repair capacity compared to those with the GG genotype [35]. However, our results were not in accord with a study performed in south China, which suggested that individuals carrying the XRCC1 rs1799782 TT genotype exhibited a reduced risk of CBP comparing to other genotypes. The XRCC1 rs25487 AA genotype was not relevant to the risk of CBP in the occupational population [11]. The possible explanation for the different conclusions is that the subjects involved in these two studies may have different genetic backgrounds due to their different geographical location in China. In addition, the sample size and constituent ratio may also explain the distinction. Although the results are not consistent, XRCC1 still has a critical function in repairing the damage caused by CBP and the XRCC1 polymorphisms may become a valid biomarker to predict the susceptibility of CBP. Furthermore, our study indicated that XRCC1 rs25487 significantly predicted the benzene toxicity, and an increased risk still existed after stratification. These meaningful results suggest that XRCC1 rs25487 G>A may be used as a valid biomarker to help identify individuals who are at high risk for CBP and prevent occupational diseases.

In our previous study, we found that ERCC1, an endonuclease in the NER system, which is located on 19q13.3, could reflect an association with the capacity to repair the benzene-induced DNA damage, and ERCC1 polymorphisms at codon 118 were associated with a difference in CPB risk. We hypothesize that other genes that are located on 19q13.2–3 could also have an effect on the risk of CBP. Therefore, we also determined whether PPP1R13L and CD3EAP polymorphisms were valid biomarkers, in addition to XRCC1. Several epidemiological studies had demonstrated that PPP1R13L rs1005165 and CD3EAP rs967591 were related to an individual’s susceptibility to cancer [23, 36, 37]. One study detected polymorphisms in several genes related to apoptosis in patients with early stage non-small-cell lung cancer and found that PPP1R13L rs1005165 was associated with a difference in the survival rate [36]. The evidence indicated that rs967591G>A affects CD3EAP expression and thus impacted the survival of patients with early stage non-small-cell lung cancer [23]. Over-expression of PPP1R13L suppressed the function of p53, which is a well-known tumor suppressor protein that plays a central role in mediating cellular responses to DNA damage [38, 39]. It is still an interesting question of whether PPP1R13L could affect the susceptibility to CBP, and additional studies are needed to further explore the role of PPP1R13L in cellular apoptosis and DNA repair. Very little has been confirmed about the function of CD3EAP. However, the structure of the CD3EAP coding region partially overlaps with the 3’-untranslated region of ERCC1, suggesting that CD3EAP may exert some of its functions by affecting ERCC1. Interestingly, CD3EAP has a separate reverse complementary overlap with PPP1R13L, and both of them share a promoter region. Thus, we speculate PPP1R13L and CD3EAP, together with ERCC1, may have a key role in the ability of the DNA repair machinery to repair the damage caused by benzene and its metabolites. Furthermore, a relationship between the PPP1R13L and CD3EAP polymorphisms with the risk of CBP has been observed in males, which further verifies the likelihood of the above explanation.

NER is thought to repair most DNA damage, including the DNA adducts caused by benzene and its metabolites BQ and HQ [40]. XPB, XPC and XPF are involved in the NER pathway and play an important role in repairing bulky DNA adducts. We found that the XPB rs4150441 GA and GA +AA genotypes may be associated to an increased risk of CBP. A related study suggested that XPB rs4150441 could predict an individual’s susceptibility to benzene-induced hematotoxicity at relatively low levels of benzene exposure [3]. Although polymorphisms in other NER genes have also been found be associated with benzene poisoning susceptibility in Chinese workers, we did not find any evidence indicating that XPC and XPF polymorphisms could affect an individual’s sensitivity to CBP in our current data.

A haplotype analysis was conducted in our current study to obtain much more information from a number of tightly linked SNPs. XRCC1 (rs25487, rs25489 and rs1799782) PPP1R13L rs1005165, CD3EAP rs967591, and ERCC1 (rs3212986, rs11615) are located in close proximity on chromosome 19q13, and the linkage disequilibrium of these SNPs was considered more important for indicating an individual’s DNA repair capacity. The results showed that the carriers of the XRCC1 rs25487A, rs25489G and rs1799782T haplotypes had a higher risk of CBP than those carrying the rs25487G, rs25489G and rs1799782C haplotypes. These results better explain the contribution of XRCC1 rs25487 and rs1799782 to CBP. Furthermore, ERCC1, CD3EAP and PPP1R13L, which are all located on 19q13.2–3, were identified as a high risk region that predicts the development of the disease. However, in our current study, the haplotype analysis of these four SNPs did not show a relationship between any of the haplotypes and the risk of CBP in the Chinese population. A haplotype analysis of three SNPs (XPF rs4781560, XPC rs2279017 and rs2228001) was also performed in our study, but no meaningful result was observed. It indicated that many more studies would be necessary to identify the possible mechanisms.

In conclusion, we found that the variant XRCC1 rs25487 and rs1799782 alleles may contribute to predicting the risk of CBP. We focused on the functions of these genes, located in chromosome 19q13.2–3, to identify valid biomarkers to predict the risk of CBP susceptibility. We found, for the first time, that the entire 19q13.2-19q13.3 region, containing XRCC1, PPP1R13L, CD3EAP and ERCC1, may have a particular association with CBP in occupationally exposed Chinese populations through genetic variation. Although there are several limitations in the present study, some of these SNPs showed a weak association with the risk of CBP. An increased sample size, improved experimental design and methods, systematic follow-up and deeper mechanistic study would be of interest. Other SNPs related to the DNA repair capacity that may affect the susceptibility to CBP are the subjects of further research. All valid measures will contribute to protect the individuals who are susceptible to CBP, and provide a possibility for early diagnosis and treatment.

Supporting Information

S1 Fig. Part of SNaPshot QC genotyping results.

GeneMapper electropherograms of SNaPshot reactions. Plots of size (nt) versus relative fluorescence units (rfus) for 10 DNA samples exhibiting variations at the SNP sites (PPP1R13L rs1970764 and XPF rs2020955 were not chose for our data analysis at last). The x axis represents the size (bp) of the primer pair with the incorporated nucleotides, while the y axis corresponds to the relative fluorescent units of the peak. Each fluorescent dye corresponds to a different nucleotide: blue represents G, green represents A, red represents T, and black represents C. The orange peak represents the size standard.



We thank all study participants for their cooperation, for technical help, and for sample collection in this study.

Author Contributions

Conceived and designed the experiments: XL. Performed the experiments: PX SX MX QZ XZ. Analyzed the data: PX GZ. Contributed reagents/materials/analysis tools: XL YC CJ JY SW. Wrote the paper: PX GZ SX. Collected the samples: LG.


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