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Eur Respir J 2005; 26:133-139
Copyright ©ERS Journals Ltd 2005

Airflow limitation and changes in pulmonary function among bleachery workers

A. J. Mehta1, P. K. Henneberger1, K. Torén2 and A-C. Olin2

1 Division of Respiratory Disease Studies, National Institute for Occupational Safety and Health, Centers for Disease Control and Prevention, Morgantown, WV, USA. 2 Sahlgrenska University Hospital, Goteborg, Sweden.

CORRESPONDENCE: P. Henneberger, Division of Respiratory Disease Studies, National Institute for Occupational Safety and Health, 1095 Willowdale Road, Morgantown, WV 26505, USA. Fax: 1 3042855820. E-mail: pkh0@cdc.gov

Keywords: Airways disease, ozone exposure, pulmonary function, pulp mill workers

Received: June 12, 2004
Accepted March 17, 2005


   ABSTRACT
TOP
 ABSTRACT
MATERIALS AND METHODS
 RESULTS
 DISCUSSION
 REFERENCES
 
This study investigated whether chronic airflow limitation and rapid decline in pulmonary function were associated with peak exposures to ozone and other irritant gases in pulp mills.

Bleachery workers potentially exposed to irritant gassings (n = 178) from three Swedish pulp mills, and a comparison group of workers not exposed to irritant gassings (n = 54) from two paper mills, were studied. Baseline surveys occurred in 1995–1996, with follow-up surveys in 1998–1999. Participants performed spirometry and answered questions regarding ozone, chlorine dioxide (ClO2), and sulphur dioxide (SO2) gassings.

From regression models controlling for potential confounders, declines in both the forced expiratory volume in one second (FEV1) (–24 mL·yr–1) and the forced vital capacity (FVC) (–19 mL·yr–1) were associated with ClO2/SO2 gassings. At follow-up, the prevalence of chronic airflow limitation (i.e. FEV1/FVC less than the lower limit of normal) was elevated for participants with only pre-baseline ozone gassings and with both pre-baseline and interval ozone gassings, after controlling for potential confounders.

These findings suggest that obstructive effects among bleachery workers are associated with ozone gassings, and that adverse effects on spirometry might also accompany chlorine dioxide/sulphur dioxide gassings. Peak exposures to irritant gases in pulp mills should be prevented.

Pulp mill workers, especially those involved in the bleaching process, have the potential for exposure to a variety of irritant gases that include sulphur dioxide (SO2), chlorine (Cl), and chlorine dioxide (ClO2) 1. Epidemiological studies have found that pulp mill workers with peak exposures to Cl and other irritant gases have an increased risk for reduced lung function 2–5. Starting in the early 1990s, some Swedish pulp mills began replacing Cl and ClO2 with ozone as a bleaching agent 6. Workers in these settings most likely experience low-level background exposure to ozone, as well as episodic high-level exposure due to accidental gassings.

Ozone is a known respiratory irritant, and short-term exposure to ozone can cause increased airways responsiveness and inflammation 7. Studies conducted in non-occupational settings provide mixed evidence that exposure to ozone can lead to decrements in lung function. Experimental chamber exposure studies with healthy human subjects have demonstrated that ozone-induced respiratory symptoms and decrements in lung function are a function of exposure concentration, minute ventilation during exposure, and duration of exposure, and that response to ozone decreases with age 8, 9. Epidemiological studies conducted in the USA revealed that the onset of asthma in nonsmoking adult males was associated with long-term ambient concentrations of ozone in air pollution 10, 11. In the initial cross-sectional survey of a community-based study, participants with elevated ambient exposures to photochemical oxidants were at greater risk for low lung function 12. Investigators followed a subset of the same cohort over 8–10 yrs and found that an accelerated decline in lung function was associated with neither chronic ambient exposures to ozone nor an acute response to ozone in a laboratory setting 13.

The evidence for an ozone-lung function relationship is also mixed and is based on studies of pulp mill workers in Sweden that were conducted in the mid- and late-1990s. In a study at one Swedish pulp mill, investigators found increased exhaled nitric oxide among bleachery workers reporting ozone gassings, suggesting airways inflammation may have been present 14. The investigators also reported that the forced expiratory volume in one second (FEV1) was lower for bleachery workers compared with process workers from the adjacent paper mill (97.6% versus 104.0% predicted; p = 0.007), while there was no difference between the two groups in forced vital capacity (FVC) 14. When comparisons were limited to the bleachery workers, those who reported ozone gassings did not have lower FEV1 or FVC. In a subsequent study, these data were combined with comparable data that had been gathered from workers at a second Swedish pulp and paper mill operation where ozone was used. The FEV1 was only marginally reduced for the bleachery workers compared with their paper-mill counterparts (p = 0.19) 15. In another round of field studies conducted several years later, the sample size was increased by including workers from a third pulp mill that used ozone. The bleachery workers who reported at least four ozone gassings had a lower FEV1 than the comparison paper mill workers (99.9% versus 105.3% pred), but this difference was not statistically significant (p = 0.17) 16.

The current authors sought to further explore the relationship between ozone exposure and lung function by conducting additional analyses of data from the three pulping operations in Sweden. In particular, longitudinal change in pulmonary function, which might be a more accurate indicator of the effect of gassings than the cross-sectional analyses that have been published, was examined. Also, it was investigated whether those who reported gassings were more likely to have chronic airflow limitation.


   MATERIALS AND METHODS
TOP
 ABSTRACT
 MATERIALS AND METHODS
RESULTS
 DISCUSSION
 REFERENCES
 
The bleachery and paper mill workers identified for this study had participated in field studies conducted in the 1990s 15–17. During 1995–1996, researchers invited all process, maintenance, and laboratory workers in the bleaching departments (n = 240) from three sulphate pulp mills to participate in a medical survey 15, 17. Of those invited, 76% of the bleachery workers (n = 183) performed spirometry testing. Using the same methods at follow-up surveys during 1998–1999 16, 179 bleachery workers repeated spirometry testing. One bleachery worker was excluded as an outlier for body weight, which left a total of 178 bleachery workers (74%) in the exposed group whose data were included in the final analyses of the present study. Researchers established a comparison group by inviting process workers (n = 93) from two adjacent paper mills to participate in the 1995 and 1996 surveys 15. Of those invited, 63 of the paper mill workers performed spirometry testing. At follow-up during 1998–1999 16, 62 paper mill workers (67%) repeated spirometry testing. Eight paper mill workers were excluded because they reported a history of gassings while working in pulp mills, which left a total of 54 paper mill workers (58%) for final analysis in this study. More details about the study population are documented in previous articles 15–17.

Exposure assessment
Cl and/or ClO2 was used as a bleaching agent in each of the three pulp mills (Mills A, B, C) starting in the 1950s, but they were replaced with ozone in 1995 at Mill A, 1993 at Mill B and 1992 at Mill C. Workers were still exposed to other irritant gases after the introduction of ozone. SO2 is still used in one of the pulping operations in Mill A. Production of hypochlorite in that mill, which results in potential exposure to Cl gas, was stopped in 1998. SO2 and ClO2 are still used in Mill B, while Mill C ended use of these compounds in 1995. Workers in paper mills are not typically exposed to irritant gases.

The concentration of ozone in a pulp mill is low (<40 ppb) under normal conditions, but can briefly be very high (>10,000 ppb) during accidental gassings 15. In 1995 and 1996, stationary measurements of ambient ozone concentrations were conducted in Mills B and C for 366 days in two rooms that are critical areas for high ozone exposure. On 6 of the 366 days, ozone levels exceeded 900 ppb 15. Stationary measurements probably were not representative of personal exposures during gassing events. Consequently, personal exposure to ozone gassings was based on each subject's self-report during the follow-up survey in 1998–1999, and was defined as a positive response to the following question. "Have you been exposed to ozone with coughing, wheezing, breathlessness or pain in the chest as a result? If "yes," when did this occur?". Based on the subjects' recall to the second question, the year of the ozone gassing event was recorded to determine whether it occurred prior to, or during the interval period. A negative response for exposure to ozone gassing was assigned if the subject did not report the year in which the gassing event occurred. Similar pairs of questions from the baseline survey in 1995–1996 and the follow-up survey in 1998–1999 were used to identify participants with a history of exposure to ClO2 and SO2 gassings, to control for the effect of other irritant gassings while estimating the effect of ozone. Exposure to ClO2 and SO2 gassings were summarised into a single indicator variable that was positive if the person had experienced a gassing event due to either ClO2 or SO2. Irritant gassing exposure was summarised using the following categories: 1) Bleachery workers, reported gassings including ozone gassings (further divided by timing of gassings: pre-baseline survey and/or during the interval between baseline and follow-up surveys) and ClO2/SO2 gassings. 2) Bleachery workers, no reported gassings. 3) Paper mill workers (no irritant gassings).

Outcome assessment
All of the subjects underwent baseline spirometry in 1995–1996 and follow-up spirometry in 1998–1999. The spirometry tests were administered by the same team of research nurses using the same equipment (dry-wedge spirometer; Vitalograph®, Buckingham, UK) at baseline and at follow-up. Each subject performed at least three technically acceptable trials, and the largest values for FVC and FEV1 were retained and compared with predicted values 18. Details of spirometry measurements are documented in previous studies 14, 15.

Each subject's average annual changes in FEV1 ({Delta}FEV1), FVC ({Delta}FVC), and FEV1/FVC ({Delta}FEV1/FVC) were calculated using the following equation:


{erj260133E001}

Chronic airflow limitation was defined as FEV1/FVC less than the lower limit of normal (LLN) at the follow-up survey 19. A fixed FEV1/FVC ratio (e.g. FEV1/FVC <70%) was used, as the LLN is not recommended in adults because FEV1/FVC is inversely related to age and height 19. One statistically acceptable approach for establishing lower limits for any spirometric measure is to define the lowest 5% of the reference population as below the LLN 19. For the current study, the FEV1/FVC value of the fifth percentile was estimated as:


{erj260133E002}

Where RSD is the residual standard deviation constant derived from reference population 18.

The reference population, from which the predicted values and numeric RSD constant are derived, consisted of healthy adult males and females from Sweden 18.

Statistical analysis
Univariate tests for statistical significance were accomplished using Fisher's exact test or a continuity-corrected Chi-squared test for categorical variables, and an unpaired t-test for continuous variables 20.

Using linear regression 21, baseline and follow-up FEV1, FVC, and FEV1/FVC ratio, and {Delta}FEV1, {Delta}FVC, and {Delta}FEV1/FVC, were modelled as continuous outcomes against exposure class dummy variables controlling for potential confounders. The exposure class dummy variables represented the gassings that were reported to have occurred pre-baseline and during the interval, according to the outcome that was being modelled. Paper mill workers served as the reference group. Potential confounders included age, sex, average weight, average height, smoking status, and pack-yrs smoked, as well as baseline spirometry for the models of longitudinal change. The averages of weight and height as potential confounders were used to resolve minor differences between baseline and follow-up measurements. For subjects who were missing recorded weight values at baseline (n = 14), the single recorded weight value at follow-up was used instead of the average. Age and smoking variables were as of the baseline or follow-up survey for the models of cross-sectional spirometry. For longitudinal change in spirometry, age was the mean of baseline and follow-up ages, smoking status was during the interval, and pack-yrs smoked was the total at the end of the interval.

For chronic airflow limitation at follow-up, prevalence ratios were calculated to express the effect of occupational exposure. Prevalence ratios were chosen, rather than odds ratios, because they are more conservative and interpretable relative to incident rate ratios 22. Since relatively few workers fulfilled the criteria for chronic airflow limitation, the number of potential confounders was limited by conducting forward and backward stepwise model fitting. The potential confounders were the same as those used in the linear regression models: age at follow-up, sex, average weight, average height, smoking status at follow-up, and pack-yrs smoked by follow-up. There were separate indicator variables for current and former smoking, but they were both retained in the model if one of them fulfilled the criteria for inclusion. The exposure variables were always in the model. Other covariates were included with a p-value ≤0.10 and excluded if p>0.20. If a covariate had a p-value 0.10–0.20, it was tested further by removing it from the model to see whether this caused a change of ≥15% in the effect estimates for the relevant exposure variables. If such a change was observed then it was kept in the model. The final models from forward and backward model fitting were compared and the model with more covariates was used.


   RESULTS
TOP
 ABSTRACT
 MATERIALS AND METHODS
 RESULTS
DISCUSSION
 REFERENCES
 
Of the 232 participants included in the study, there were 54 paper mill workers with no exposure to irritant gassings (23%) and 178 bleachery workers with potential exposure (77%). The mean interval period (i.e. time between baseline and follow-up spirometry tests) for all participants was 3.4 yrs (SD = 0.7). At follow-up, 124 bleachery workers reported irritant gassings, but only 61 bleachery workers reported gassings that occurred during the interval period. The sample sizes in the irritant gassing exposure classes at baseline and during the interval period are presented in tables 1Go and 2Go, respectively. Of the 66 bleachery workers who had reported ozone gassings by follow-up, 31 reported only gassings that occurred prior to baseline, 16 reported only gassings that occurred after baseline, and 19 reported gassings that occurred during both periods.


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  		Table. 1— Mean per cent predicted FEV1 and FVC, and mean FEV1/FVC ratio at baseline for all participants and by exposure status

 

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  		Table. 2— Regression models for{Delta}FEV1, {Delta}FVC, and {Delta}FEV1/FVC during interval#

 
The mean±SD age, average weight and average height for all participants were 43.7±8.6 yrs, 83.3±11.6 kg, and 178.0±7.4 cm, respectively. There were no statistically significant (p<0.05) differences in these variables between the bleachery exposure classes (at baseline, during the interval, or at follow-up) and the paper mill workers. Mean pack-yrs smoked at baseline and follow-up for all participants were 6.2±9.5 and 6.5±10.1, respectively. Bleachery workers with ozone gassings both pre-baseline and during the interval had a lower mean pack-yrs at follow-up than paper mill workers (p<0.05).

Only 13% (n = 31) of the participants were current smokers by follow-up; 37% (n = 86) were former smokers. There were no statistically significant differences in current and former smoking between the bleachery exposure classes and paper mill workers. The participants were predominantly male (n = 211; 91%); bleachery workers who reported ClO2/SO2 gassings pre-baseline or during the interval were less likely to be female in comparison with paper mill workers (p<0.05).

The mean±SD baseline spirometry values for all 232 participants were 4.13±0.7 L FEV1, 5.19±0.9 L FVC, and 79.6±5.9% FEV1/FVC. The mean per cent predicted FEV1 and FVC, and the mean FEV1/FVC ratio at baseline for all participants and by exposure status are presented in table 1Go. The only pre-baseline ozone gassings category had the lowest per cent predicted values. When regression models were fitted for FEV1 and FVC, with paper mill workers as the comparison group and variables included to control for confounding, none of the coefficients for exposure reached the level of statistical significance (i.e. p≤0.05) (models not shown). The variable for pre-baseline ozone gassings attained borderline statistical significance in the regression model for FEV1 with a coefficient of –139 mL (p = 0.098), but not in the model for FVC (–128 mL, p = 0.20). The coefficients for pre-baseline ClO2/SO2 gassings from the same models were +51 mL (p = 0.52) for FEV1 and +57 mL (p = 0.55) for FVC. The mean values for the FEV1/FVC ratio varied little among the different exposure classes (table 1Go), and the same was observed in the regression model for this outcome (model not shown).

From the longitudinal regression models (table 2Go), declines of –24 mL·yr–1 FEV1 (p = 0.01) and –19 mL·yr–1 FVC (p = 0.11) were associated with ClO2/SO2 gassings (models A and B). The 31 workers who reported ozone gassings by baseline, but not during the interval between baseline and follow-up, had positive coefficients of +22 mL·yr–1 FEV1 (p = 0.054) and +25 mL·yr–1 FVC (p = 0.10). The workers who reported that ozone gassings occurred only during the interval had a positive coefficient of +0.44%·yr–1 (p = 0.10) for FEV1/FVC (model C, table 2Go). The rate of decline of FEV1/FVC was greatest for workers with both pre-baseline and interval ozone gassings (–0.34%·yr–1), although it was not statistically significant (p = 0.19).

There were no statistically significant associations between spirometry at follow-up and gassing exposures after controlling for potential confounders (regression models not shown). The only finding of borderline statistical significance was for study participants with both pre-baseline and interval ozone gassings, with a coefficient of –217 mL FEV1 (p = 0.095).

Nineteen workers were classified as having chronic airflow limitation at follow-up, or 8.2% of the 232 participants. They had a mean per cent predicted±SEM FEV1 at follow-up of 88.3±3.7%. Only three of the 19 workers had FEV1 <80% pred; therefore, most of these workers had borderline obstructive disease 18. The distribution by exposure class of these 19 workers is presented in table 3Go. The prevalence was lowest for paper mill workers (3.7%) and highest for workers with only pre-baseline ozone gassings (16.1%) and both pre-baseline and interval ozone gassings (15.8%). In the regression model for chronic airflow limitation (table 4Go), these two ozone gassing categories had elevated prevalence ratios of 4.3 (95% confidence interval (CI) 1.2–15.7) and 5.5 (95% CI 1.1–28.0), respectively. There was no evidence of interaction between these variables for ozone gassings and the variables for potential confounders in the model. None of the other gassing variables, including the one for only interval ozone gassings, had a prevalence ratio that was elevated and statistically significant. Thus, the pre-baseline exposures, but not the interval exposures, appeared to be responsible for the relationship between ozone gassings and chronic airflow limitation.


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  		Table. 3— Chronic airflow limitation at follow-up by exposure class#

 

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  		Table. 4— Regression model for chronic airflow limitation at follow-up#

 

   DISCUSSION
TOP
 ABSTRACT
 MATERIALS AND METHODS
 RESULTS
 DISCUSSION
REFERENCES
 
In the current study, bleachery workers who reported only pre-baseline ozone gassings or a combination of pre-baseline and interval ozone gassings were more likely to have chronic airflow limitation at follow-up than nongassed paper mill workers. Although most of the study participants classified with chronic airflow limitation had borderline obstructive disease, they might be at risk for subsequent adverse outcomes. In particular, a recent analysis of the first National Health and Nutrition Examination Survey (NHANES I) population found that mild chronic obstructive pulmonary disease (COPD) (FEV1/FVC <70% and FEV1 ≥80% pred) was associated with excess mortality 23.

From the regression models for the baseline survey, the bleachery workers who reported ozone gassings tended to have lower values for FEV1, but this was not observed for their co-workers who had reported gassings due to ClO2/SO2. This difference at baseline could have been the result of unmeasured differences in the levels of exposure that occurred during gassing events. Specifically, it is likely that high exposures accompanied the onset of ozone use prior to the baseline survey. When Mills B and C began to use ozone in the 1990s, they were not prepared for its strong corrosive properties, which led to numerous leaks and pipe breaks 6. In at least one of the two mills, the workers identified as most exposed to ozone developed chronic bronchiolitis 16. Also, the workers who had suffered the adverse effects of ClO2/SO2 gassings might have left the work force over the years and not have been available for testing (i.e. selection bias). Ozone had been used for a relatively short period of time, and there might have been less loss of workers affected by ozone peak exposures.

The absence of substantial longitudinal declines in FEV1 and FVC associated with post-baseline ozone gassings might reflect improvements in the control of ozone exposure during the interval. In contrast, bleachery workers who reported pre- or post-baseline ClO2 or SO2 gassings experienced declines in FEV1 and FVC during the interval period. When {Delta}FEV1 and {Delta}FVC were modelled with ClO2 and SO2 gassings represented by separate variables, elevated declines in FEV1 and FVC in comparison with paper mill workers were seen mainly in bleachery workers who reported ClO2 gassings (data not shown).

As described in the Introduction, previous cross-sectional studies based on subsets of the current cohort did not consistently find an association between lower pulmonary function and bleachery work or ozone gassings 14–16. Other cross-sectional studies on pulp mill workers have found an association between airflow obstruction and gassings to Cl or ClO2 2, 4–5. Further cross-sectional studies have observed concurrent decrements in FEV1 and FVC in workers exposed to SO2 or Cl gases 3, 24, 25 or to acetic acid 26. The concurrent decrements might reflect hyperinflation with an increased residual volume and, thus, not be indicative of a true restrictive disorder. Industry-based epidemiological studies have also shown that occupational exposure to inorganic and organic dusts and to chemical agents can cause COPD 27–29.

Respiratory health effects due to occupational exposure to ozone have been reported for other occupational groups, including welders and outdoor workers 30–34. Welders, who in certain processes are exposed to high levels of ozone and nitrogen oxide, have been reported to have lower pulmonary function and higher prevalence of work-related respiratory symptoms than nonwelders 31, 32, but one longitudinal study reported no association between ozone exposure and accelerated decline in lung function 30. From a community-based cross-sectional survey, participants (both smokers and nonsmokers) with high ambient exposures to photochemical oxidants were more likely to have FEV1 and FVC <50% pred compared with participants with low ambient exposures 12. However, when the investigators retested a subset of this cohort, nonsmoking adults with elevated ambient ozone exposures did not have an accelerated longitudinal decline in FEV1 or FVC over an 8–10-yr period 13.

Some features of the current study design may have minimised the ability to detect a significant ozone exposure-related longitudinal change in lung function. While the exposure history for ozone included the period beginning from onset of ozone use in the pulp mills during the early-to-mid-1990s up to the follow-up survey in 1998–1999, spirometry testing of the workers began in 1995–1996. Unfortunately, spirometry data for study participants at the start of ozone use is not available, with the exception of Mill A. When similar longitudinal analyses comparing pulp mill workers in Mill A with paper mill workers from Mills B and C were ran, the effect of ozone gassings was no more than when all pulp mill workers were included (data not shown). The follow-up spirometry values should reflect all work-related effects up to that point and, therefore, are the most appropriate outcomes when examining the effect of ozone gassings since onset of use.

Based on the work of other researchers, the current study may have needed more subjects and additional serial pulmonary function testing to observe a significant work-related effect for ozone over a 3–4-yr period 35. While paper mill workers, selected as the internal control group, did not experience gassing events, they were exposed to paper dust, which has been previously shown to be associated with lower respiratory symptoms and impaired lung function 1, 36. Thus, the ability to detect an effect of gassings may have been reduced.

A loss to follow-up can bias findings towards the null in any longitudinal study. This may have occurred in the current study if bleachery workers who developed respiratory problems during the study period had left the pulp mill and were therefore not included in the study. However, there was little opportunity for this problem because only four of the bleachery workers tested in 1996 did not complete testing in 1999. Recall bias can also occur in studies that derive exposure data by questionnaires if recall of those data varies by disease status. It might have occurred in the current study if bleachery workers with more severe lung function abnormalities were more likely to recall irritant gassing incidents. A gassing event was counted if the worker experienced acute respiratory symptoms. Someone who had acute respiratory symptoms after a high-exposure event might have been more susceptible than a co-worker who had the same exposure but did not have symptoms. Since 70% of the bleachery workers reported being gassed by ozone and/or ClO2/SO2, it seems that they included many more people than the subset of the study population that was susceptible. Still, those susceptible to irritant gassings might have been over-represented in the gassed group, which could have biased the effect estimates away from the null.

In conclusion, bleachery workers who reported either pre- or post-baseline chlorine dioxide/sulphur dioxide gassings were at elevated risk for declines in forced expiratory volume in one second and forced vital capacity during the interval between baseline and follow-up. While ozone gassings were not associated with a rapid decline in pulmonary function during the study period, bleachery workers who reported ozone gassings prior to the study period were more likely to have chronic airflow limitation at follow-up. The findings suggest that obstructive effects among pulp mill workers are associated with ozone gassings, and that adverse effects on spirometry might also accompany chlorine dioxide/sulphur dioxide gassings. Peak exposures to irritant gases in pulp mills should be prevented.


   REFERENCES
TOP
 ABSTRACT
 MATERIALS AND METHODS
 RESULTS
 DISCUSSION
 REFERENCES
 

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