A panel study of occupational exposure to fine particulate matter and changes in DNA methylation over a single workday and years worked in boilermaker welders
© Kile et al.; licensee BioMed Central Ltd. 2013
Received: 7 October 2012
Accepted: 4 June 2013
Published: 11 June 2013
Exposure to pollutants including metals and particulate air pollution can alter DNA methylation. Yet little is known about intra-individual changes in DNA methylation over time in relationship to environmental exposures. Therefore, we evaluated the effects of acute- and chronic metal-rich PM2.5 exposures on DNA methylation.
Thirty-eight male boilermaker welders participated in a panel study for a total of 54 person days. Whole blood was collected prior to any welding activities (pre-shift) and immediately after the exposure period (post-shift). The percentage of methylated cytosines (%mC) in LINE-1, Alu, and inducible nitric oxide synthase gene (iNOS) were quantified using pyrosequencing. Personal PM2.5 (particulate matter with an aerodynamic diameter ≤ 2.5 μm) was measured over the work-shift. A questionnaire assessed job history and years worked as a boilermaker. Linear mixed models with repeated measures evaluated associations between DNA methylation, PM2.5 concentration (acute exposure), and years worked as a boilermaker (chronic exposure).
PM2.5 exposure was associated with increased methylation in the promoter region of the iNOS gene (β = 0.25, SE: 0.11, p-value = 0.04). Additionally, the number of years worked as a boilermaker was associated with increased iNOS methylation (β = 0.03, SE: 0.01, p-value = 0.03). No associations were observed for Alu or LINE-1.
Acute and chronic exposure to PM2.5 generated from welding activities was associated with a modest change in DNA methylation of the iNOS gene. Future studies are needed to confirm this association and determine if the observed small increase in iNOS methylation are associated with changes in NO production or any adverse health effect.
KeywordsDNA methylation PM2.5 iNOS Welders LINE-1 Alu Boilermakers
Boilermakers are skilled welders who cut and weld metal plates. They use a variety of welding technologies including oxyacetylene gas torches, gas tungsten arc welding, shielded metal arc welding, or gas metal arc welding. The extreme heat produced by welding generates a complex mixture of gases, aerosols and particulate matter. This molten mixture condenses into ultrafine and fine particulate matter with an aerodynamic diameter ≤ 2.5 μm (PM2.5) that is easily inhaled . Welding fumes are rich in metal oxides and can contain antimony, beryllium, cadmium, chromium, cobalt, copper, iron, lead, manganese, mercury, molybdenum, nickel, vanadium, and zinc [2, 3] although the exact composition of welding fumes will depend on many factors including base metal characteristics and type of welding.
Epidemiological studies show that chronic exposure to welding fumes are associated with respiratory health effects including cardiovascular disease, asthma, bronchitis, lung function changes, and increased risk of lung cancer [4–10]. While the mechanisms linking welding fume exposure to adverse health outcomes is not fully understood, previous studies implicate several biological pathways for welding fume toxicity including oxidative stress , systemic inflammation [12–14], and alterations in cardiac autonomic responses [4, 15, 16]. It is also possible that welding fumes alter epigenetic mechanisms and subsequently gene expression. Data from previous studies shows that many of the metals detected in welding fumes including nickel, lead, cadmium, chromium, beryllium, and arsenic are associated with altered DNA methylation [17–27]. There is also evidence that exposure to particulate matter air pollution is associated with altered DNA methylation [28–31]. Changes in DNA methylation have been observed in subjects with cardiovascular disease and cancer . Thus, it is possible that epigenetic changes may provide a potential mechanism by which welding fumes are linked to adverse biological effects.
We, therefore, hypothesized that exposure to particulate matter generated from welding activities can alter DNA methylation. This hypothesis was tested in boilermakers who were previously recruited for a panel study designed to evaluate the cardiopulmonary health effects of welding fumes [4, 15]. We used existing data to explore the relationship between exposure to PM2.5 and DNA methylation over time because individuals provided blood samples collected both pre- and post-work shift, had personal PM2.5 occupational exposure measurements, and detailed work histories. Specifically, we hypothesized that exposure to PM2.5 over a single work shift would be associated with changes to DNA methylation, as well as, from cumulative exposure based on years worked as a welder.
We employed a candidate gene approach and measured DNA methylation in short interspersed nucleotide elements (Alu) and long interspersed nucleotide elements (LINE-1). These two repetitive elements make up approximately 55% of the human genome and are heavily methylated to suppress their expression . Repetitive elements are activated during conditions of cellular stress and de-methylation of LINE-1 and Alu elements increase their activity as retrotransposable sequences [34–36]. Additionally, we quantified DNA methylation in the inducible nitric oxide synthase gene (iNOS, also known as NOS2, Genbank accession number AF017634) which is involved in the production of nitric oxide and plays an important role in a variety of cardio-pulmonary processes including asthma , chronic obstructive pulmonary disease , and cardiovascular health .
The Institutional Review Board at the Harvard School of Public Health approved the study protocol and informed consent was obtained prior to participation. The details of participant selection and study recruitment have been described previously [4, 15]. This analysis used samples collected from 38 individuals who had archived whole blood samples available for DNA extraction. Briefly, boilermaker construction workers were monitored on a high-exposure welding day and low-exposure non-welding days at the Union welding school in 2003 and 2008 as part of a panel study on welding fumes and cardiovascular risk. On non-welding days, participants performed office work in a large enclosed break room adjacent to the welding room. Per the initial study design, boilermakers were allowed to participate on multiple occasions in each observation period. We observed that two boilermakers participated in both 2003 and 2008 and three boilermakers participated twice on different days in 2008. Not all participants opted to provide a post-shift blood sample. Therefore, this analysis utilized 40 blood samples collected in the morning prior to the start of a work-shift (pre-shift) and 38 blood samples were collected in the afternoon after all work activities had been completed (post-shift). Also, twenty-four individuals provided two blood samples on the same observation day (pre- and post-shift). The most common type of welding was manual metal arc welding on mild (manganese alloys) and stainless steel (chromium and nickel alloys) bases. All welding was performed in a room outfitted with 10 workstations, each with local exhaust ventilation.
A modified American Thoracic Society questionnaire was used to collect information on socio-demographic information, smoking history, occupational history and medical history .
All individuals wore personal gravimetric particulate samplers over the duration of the work shift using a KTL cyclone (GK2.05SH, BGI Incorporated, Waltham, MA) with an aerodynamic diameter ≤2.5 μm used in line with a pump drawing 3.5 L/min of air. The inlet tubing was secured to the participant’s shoulder in the breathing zone area. Exposure to PM2.5 was measured over a six-hour welding shift or equivalent non-welding period as previously described by Cavallari et al. . All samples were blank corrected. Two individuals were missing PM2.5 data. Air quality monitoring was performed on the same day as blood sample collection.
Primers and location of CpG sites that were quantified by pyrosequencing
(5′ to 3′)
(5′ to 3′)
(5′ to 3′)
Global methylation analysis
G/A C/TG/A C/TG/ A CCACCA
TTC/T GTGGTGC/T GTC/T G
Gene-specific methylation analysis
C/T GAGTC/T GAAAATTGAGGTTTC/T GG
The average %mC was calculated for 3 CpG sites in LINE-1, 3 CpG sites in Alu, and 4 CpG sites in iNOS. Linear mixed effects regression models with a repeated statement to account for repeated measurements on the same subjects were used to evaluate the relationship between %mC and PM2.5; as well as, the relationship between %mC and the number of years each individual worked as a boilermaker. Separate models were constructed for LINE-1, Alu, and iNOS. In the models that looked at cross-shift PM2.5 exposure, pre-shift blood %mC for each gene was included as a predictor in the models to control for individual factors that may influence methylation. Whereas, pre-shift blood %mC was not included in the models that evaluated the relationship between the number of years a person reported working as a boilermaker and methylation. All models were adjusted for smoking (yes/no), wearing a respirator (yes/no), and age. Since age was highly collinear with the number of years a person worked as a boilermaker (σspearman=0.57), we used the residuals from a regression model that had age as the dependent variable and years worked as a boilermaker to adjust for age (ageRS) in models that looked at the association between methylation and chronic exposure. All analyses were performed with SAS version 9.2.
Description of selected characteristics in 38 boilermakers at the time of their first recruitment
Mean (SD) or Percent
Years worked as boilermakerb
1 - 35
Exposure characteristics c
Median (IQR) or Percent
PM2.5 exposure (mg/m3)c
Weld day samplesd
Description of DNA methylation for the repeated blood sample measurements
Association between PM 2.5 exposure across the work shift (mg/m 3 ) and methylation of Alu , LINE-1 and iNOS measured in whole blood collected post-shift
Global DNA Methylation
Gene specific DNA Methylation
Association between years as a boilermaker and methylation of Alu, LINE-1 and iNOS measured in all whole blood samples
Global DNA Methylation
Gene specific DNA Methylation
Association between years as a boilermaker and methylation of Alu, LINE-1 and iNOS measured in only in pre-shift whole blood samples
Global DNA Methylation
Gene specific DNA Methylation
Considering that smoking was common in this population and might be an effect modifier of iNOS methylation, an interaction term between years worked as a boilermaker and current smoking was also evaluated in the model. This interaction term was not significant which indicated that there was no effect modification by smoking status (βinteraction = 0.10, SE: 0.09, p-value = 0.31).
We observed that occupational exposure to fine particulate matter generated from welding activities measured across a single work-shift was associated with modest increases in DNA methylation in the promoter region of the inducible nitric oxide synthase gene in whole blood DNA. The number of years worked as a boilermaker was also associated with modest increased DNA methylation in the iNOS gene. However, we did not observe any relationship between acute exposure to welding fume PM2.5 or years worked and DNA methylation in two repeated elements, Alu and LINE-1. These findings suggest that methylation of the iNOS gene may be mutable over short periods of time.
DNA methylation regulates gene expression with increased methylation leading to gene silencing. Biologically, it is plausible that iNOS could be influenced by exposure to PM2.5 generated from welding activities. Animal models show that acute exposure to welding fumes produce reactive oxygen species and inflammatory cytokines including tumor necrosis factor-alpha and interleukin-1 beta [5, 40]. In turn, these immunologic and inflammatory factors stimulate inducible nitric oxide synthase which produces nitric oxide (NO) which can constrict vascular beds, produce hypertensive responses, regulate nonspecific host defenses, and modulate inflammation [41, 42]. These effects appear to depend on the PM composition. For instance, PM derived from urban sources diminished NO production, whereas, respirable cristobalite, fine particulate matter with enriched polycyclic aromatic hydrocarbons, aerosols derived from wildfire smoke, and traffic-generated PM increased NO production [43–45]. There is also evidence that welding fume PM2.5 influences NO production. Prior epidemiological research by our group showed that the fractional concentration of expired breath nitric oxide decreased after five days of exposure to welding-related PM2.5 and that the decreases in expired NO were associated with the soluble metal fraction in the PM2.5. This inhibition in exhaled NO would be consistent with diminished expression of genes involved in the synthesis of NO.
Other environmental epigenetic studies have also investigated the association between particulate matter air pollution and DNA methylation in the iNOS gene. For instance, Tarantini et al. reported that particulate matter with aerodynamic diameters < 10 μm (PM10) was associated with a 0.61% decrease in methylation in the iNOS gene measured in whole blood DNA across a 3-work day period in a cohort of 63 foundry workers . Another study reported that 7-day average ambient PM2.5 was associated with decreased iNOS methylation (0.30% decrease in iNOS per 5 μg/m3 increase in ambient PM2.5) in DNA extracted from buccal cells collected from 940 children who resided in the Los Angeles area . Both of these studies observed an inverse association between increased particulate matter exposure and decreased DNA methylation in the iNOS gene. Whereas, our study observed a positive association between increased PM2.5 and increased DNA methylation in the iNOS gene. It is not clear why the direction of the effect differs between our study and the two previous studies but it is worth noting we measured different CpG sites within the promoter region of the iNOS gene and perhaps different CpG sites even within the same promoter region respond differently to environmental stimuli. Also, the composition of the particulate matter likely differed between the studies. It is also possible there was an uncontrolled confounding by smoking and/or second hand smoke exposure. As such, it is difficult to draw direct comparisons between the three studies.
We recognize that there are several limitations to our study. Methylation is tissue specific and we used DNA extracted from whole blood which is a mixture of different white blood cell types. Ultrafine particles diffuse across the alveoli and enter the bloodstream where they exert a direct effect on white blood cells by triggering an immune response. Since we did not measure white blood cell counts or measure DNA methylation in specific white blood cell sub-populations we cannot rule out that the increased iNOS DNA methylation was produced by systemic inflammation from inhaling fine particulate matter [13, 14, 48]. Another limitation of the study was that we did not collect samples that would allow for measurement of gene expression or production of nitric oxide to determine if the methylation changes in iNOS had any biological impact.
However, our study had several strengths including personal measurements of PM2.5 across the work shift which minimizes the potential for misclassification of exposure. We used pyrosequencing which is a very sensitive method and provides a quantitative measurement of DNA methylation. It is also worth noting that the blood samples were stored for several years in a cold storage facility at −80°C prior to analysis which likely reduced DNA yield but not DNA quality.
We observed a positive relationship between occupational exposure to fine particulate matter generated from welding activities and a modest increase in DNA methylation in the promoter region of the iNOS across a single work shift. We also observed a positive association between the number of years a person reported working as a boilermaker and increased DNA methylation in the iNOS gene. These results suggest that DNA methylation may be altered by PM2.5 over a short period of time. Further studies are needed that collect multiple measurements over longer periods of time to more fully understand the dynamic relationship between welding fume exposures and DNA methylation. These studies should also measure blood cell mixture to determine if the changes in DNA methylation are true epigenetic effects or a function of inflammation.
A family of short interspersed elements
Cytosine-guanine nucleotide sequence
Inducible nitric oxide synthase
Long interspersed nucleotide elements
Limit of detection
This work was supported by US NIH Grants (Funding ES00002, NIEHS K01ES017800, NIEHS ES009860, T42 OH008416, and T32 ES 07069) and HSPH-NIEHS Center Pilot Grant/New Investigator funding. Additional research support was provided by the Flight Attendants Medical Research Institute. SF was supported by the American Heart Association.
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