Mortality Among Hardmetal Production Workers: A Retrospective Cohort Study in the Austrian Hardmetal Industry : Journal of Occupational and Environmental Medicine

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Mortality Among Hardmetal Production Workers

A Retrospective Cohort Study in the Austrian Hardmetal Industry

Wallner, Peter MD; Kundi, Michael PhD; Moshammer, Hanns MD; Zimmerman, Sarah D. MS; Buchanich, Jeanine M. PhD; Marsh, Gary M. PhD

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Journal of Occupational and Environmental Medicine 59(12):p e282-e287, December 2017. | DOI: 10.1097/JOM.0000000000001046
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This study retrospectively investigates causes of death among workers of a hardmetal plant in Austria.


A retrospective cohort was formed of 1965 workers still employed in or after 1970. Follow-up was until end of 2014 based on national databases. Cobalt exposure was assessed through industrial hygiene data and urine analyses. Cox proportional hazards models were calculated for selected causes of death.


During 45,598 years of observation in total 177 deaths were observed. Forty-nine workers died from any cancer, 10 from lung cancer, and three from chronic obstructive pulmonary disease. Only the latter showed a significant association with cumulative exposure.


Although this is a young study population with little power to detect subtle effects, at least it does not indicate a pronounced cancer risk among tungsten carbide workers due to cobalt.

Occupational exposure to cobalt (Co) is considered a hazard because of its assumed carcinogenic potential, especially regarding lung cancer. The metal and its compounds have been classified as carcinogenic since the 1970s, with a general IARC1 assessment of cobalt in 1991 as “possibly carcinogenic” (Group 2B). In its Monograph 86 IARC2 rated cobalt metal with tungsten carbide as probably carcinogenic to humans (Group 2A). Also according to Austrian law3 cobalt is classified as carcinogenic. French4–6 and Swedish7 occupational cohort studies suggest that cobalt increased the risk of lung cancer, particularly in combination with tungsten carbide, in the hardmetal industry. Additionally, there is evidence that hardmetal particles exert genotoxic and carcinogenic activity.8,9

One of the main uses of Co is as a binder of tungsten carbide in hardmetals. Hardmetal dust is also a known respiratory toxicant with chronic exposure leading to scarring of the lung tissue with consecutive restrictive and also obstructive lung disease.10–12 An international consortium was set up to study the health effects of occupational exposure in the hardmetal industry in more detail.13–15 Here, we report on the results of the Austrian component of this international study.16 Reports from the US,17 UK,18 Sweden,19 and Germany20 appear as companion papers in that same issue.


Definition of the Cohort

One large Austrian hardmetal production plant (in Tyrol) agreed to participate in the cohort study. A first examination of the personnel files indicated that data were available back as far as 1950. However, a closer investigation revealed that only employees who were still working at the plant at or after 1970 had full documentation. All workers with full documentation of occupational history at the plant were included in the original cohort providing a total of 1965 workers. Most cohort members were employed at or after 1950 but a few (11 persons) have been employed even earlier (beginning between 1946 and 1949). By definition all workers were still alive in 1970. Thus, time under risk and observation started in 1970. Observation was terminated with date of death, date of leaving the country, or December 31st, 2014, whichever came first.

Because of data privacy issues only anonymous data were provided by the personnel department. Each cohort member was given a unique identifier. The researchers received the following information for each person: year and month of birth, sex, nationality, exact starting and ending dates of any job (job name, department) held at the plant, employment status (apprentice, blue collar, white collar worker). For some persons additional information (eg, known date of death) was provided.

The study was approved by the ethics committee of the Medical University of Innsbruck (AN2014–0380 345/4.9 from Janary 30, 2015). Because cohort members were anonymous and some were likely already dead informed consent was not deemed necessary for the study.

Exposure Assessment

The following data were available: Total aerosol measurements of dust (n = 130), tungsten (n = 141), and cobalt (n = 147) for the years 1985 to 2012 and urine tests of 253 persons (a total of 1166 records) from the years 2008 to 2014. Of these 1166 records 318 were from current non-smokers, 591 from current smokers, and 357 were missing that information.

In a first study21 dust, tungsten, and cobalt values were found to be highly correlated with each other. All values declined over time. In a linear regression modeling ln(Co) by time (year), monitoring method, area versus personal sampling, and dummy variables for departments a significant time trend was observed, and significant differences between some departments respectively job classes. Data were lacking on some job classes that mostly were assumed to have none or only little exposure. For some job classes exposure estimates were uncertain because of only few data points. Estimated cobalt levels (after back-transformation from logarithmic values) correlated well with measured urine levels supporting the model and time trends.

Urine concentrations of cobalt were also affected by current smoking status (higher values in smokers). Workers with missing information on current smoking status resembled non-smokers in that regard. Therefore, they most likely either did not (currently) smoke or at least were only very moderate smokers. Based on this assumption workers with urine data (usually blue collar workers with substantial cobalt exposure) did not differ substantially in current smoking status from the population of Tyrol, although they tended to be more often smokers than the white collar workers (from whom a subsample had provided smoking data through a questionnaire survey).22

Annual average exposure was estimated for each worker and every year of his/her working history based on the log-linear regression model.21 Workers from departments with missing exposure data were assigned exposure values based on expert opinion: either a department with assumed similar exposure levels was chosen or, in case of administrative departments, zero exposure was assigned.

The following exposure metrics were studied: cumulative Co exposure (mg/m3 years), duration of exposure (years), and average exposure (mg/m3). Also cumulative exposures up to 5 years and up to 10 years before end of follow-up were considered. All cumulative exposure metrics were highly correlated with each other. The alternative cumulative metrics did not lead to any meaningfully different point estimates and are, therefore, not presented.

Mortality and Cause of Death Follow-up

Information on vital status until end of 2014 and cause of death (if applicable) was at first sought through the Austrian mortality register at the Austrian National Statistics Institute, Statistik Austria. The registry received a spreadsheet file including the name and birth date of each subject together with the unique identifier. The registry added mortality date and cause of death for every match. Then the name and birth date were deleted and the final file was sent to the researchers. In order to calculate age day of birth was set to mid-month. It became obvious that this information was incomplete: some workers would have reached an implausible age. Some workers were known to have died according to the personnel department of the plant, but were missed in the mortality register. In a second approach data were compared with the central address register of Austria. This register was built around and after the year 2000. Before that date address registers were kept separately in each district. In theory old district registries have been transferred to the central register, but this procedure was likely far from complete. The register should be able to provide information if a given person is still registered in Austria and if not, when the person's permanent address was terminated and if this occurred because of death or because of relocation into a foreign country.

Many deaths already known due to the mortality register were also confirmed by the address register although the address register usually does not provide the exact date of death, but only with a precision of about 1 month. Many persons were not found in the address register and among these persons those that had died, according to the mortality register, their date of death was always in or before the year 2000. Persons missing in the address register, therefore, were primarily assumed to have died or had left Austria before or in 2000. Only for the few missing persons who had still been working in 2000 it was assumed that they were missing in the address register because of other reasons. These were, for example, persons with a German citizenship. Because the plant is located at the border to Germany they might well have worked in Tyrol, Austria and lived in Germany. They would then not be found in the Austrian address register, and for them observation had to be terminated with the end of work.

The observation of the persons was, therefore, terminated with the date of death (according to the mortality register, or, if this information was missing, according to the address register), the date they left Austria (according to the address register), the end of 2014, and, if the persons were neither found in the mortality nor in the address register, either by the end of 2000 or by the end of their work at the plant (if they still worked there after the year 2000).

Only the mortality register provided information on cause of death (1970 to 1979: ICD8; 1980 to 2001: ICD9; 2002 to 2014: ICD10). The following end-points were investigated: death according to any register data, death according to mortality register, death due to any cancer (eg, ICD10: C00 to C97), death due to respiratory cancer (eg, ICD10: C30 to C39), and death due to non-malignant respiratory disease (eg, ICD10: J00 to J99) or more specifically obstructive respiratory disease: bronchitis, emphysema, asthma (eg, ICD10: J40 to J46).

Statistical Analysis

Mortality was compared within the cohort by exposure status (internal comparison), and for the whole cohort with the general population of Tyrol (external comparison). The internal comparison was run in STATA SE 13.1 (StataCorp, College Station, TX). Three different approaches were followed:

  1. Primarily Cox proportional hazard models were run. However, time varying exposure is difficult to model in STATA. Therefore, only a single exposure metric (eg, cumulative exposure at the end of follow-up) was used in these models for each cohort member.
  2. The older a person gets the greater the chance to accumulate a higher amount of exposure. So, when using the same constant (cumulative) exposure as calculated at the end of follow-up due to reverse causality a beneficial effect of exposure could spuriously be found. In truth a person did not die earlier because he/she then still had a smaller cumulative exposure, but did not cumulate a higher exposure because of early death. Therefore, an alternative model was built using excel macros: each year under observation of each person was entered as a separate line with information on sex, age, employment status (apprentice, blue collar, white collar worker; in case of retirement the former status was kept), outcome status in that year (survived or died, selected causes of death, binary values each), nationality, and exposure metrics (average exposure in that year, cumulative exposure until that year). This table was imported into STATA and again Cox regressions conditional on age were performed.
  3. In sensitivity analyses white collar workers or all workers from Eastern European countries (mostly Turkey and former Yugoslavia) or all non-Austrian citizens were excluded. In another series of analyses only persons hired at or after 1960 were included to simulate an inception cohort. This was considered a compromise between losing too many workers with a long observation time and missing a substantial number of workers that started working after the index date (1960) but finished working before 1970.

All models were controlled for sex and Austrian citizen status. The regression models with time varying exposure were additionally controlled for working status (apprentice, blue collar worker, white collar worker).

External comparisons of the cohort with the Tyrolean population were performed in a qualitative way. For each cohort member and each year (either starting in 1970 or when they entered the cohort, whichever occurred later), the chance of survival was estimated based on sex and age-specific death-rates of the Tyrolean population in the same year. The expected survival rates of the cohort were compared with the true rates in Kaplan–Meier curves. The analyses were done for the same end-points as in the internal comparisons.


This is a young cohort with few deaths. Among the full cohort of 1965 persons, a total observation time of 45,598 years (average observation time of 23.2 years) and 177 deaths were observed. Of these, 159 were affirmed by the mortality register and cause of death was provided. Forty-nine died from any cancer, 10 from cancer of the respiratory system (all 10 lung cancer), and only three from bronchitis, emphysema, or asthma, and only one person from “other” non-malignant respiratory disease (died in the year 2000, therefore coded by ICD9 as 507.0, ie, aspiration pneumonia). As the latter was not likely associated with occupational exposure only the exposure related risk ratios for the three persons with “obstructive” respiratory diseases are reported. Including the 4th case did not alter the point estimates strongly but increased the confidence intervals.

Annual exposure was assessed by job description/department as described in Table 1. Cumulative exposures ranged from 0 to 33.5 mg/m3 years (mean ± standard deviation: 0.52 ± 2.25), average exposure from 0 to 1.8 mg/m3 (0.05 ± 0.13), and years of exposure from 0 to 45 (6.1 ± 9.0).

Annual Estimates of Personal Cobalt Concentration (mg/m3) Either Derived from21 or Based on Expert Opinion

Increased risks for death from obstructive lung diseases were seen with all exposure metrics. The findings were significant in the full data set investigating cumulative exposure. Risk estimates for all non-malignant respiratory diseases were generally similar but less precise and are not shown here. Neither increased nor decreased risks for any other mortality end-points were seen (Tables 2–4). Men tended to have higher risks than women. Austrian nationality did not significantly or systematically affect risks. Cox regression controlling for time varying exposures and job status (blue/white collar workers, apprentices) provided practically the same point estimates and similar confidence intervals.

Relative Risk (Hazard Ratio [HR] and Confidence Interval) by Cumulative Exposure (mg/m3 years) in Cox Proportional Hazards Regression; in Comparison HR from Cox Regression with Annually Changing Exposure Status
Relative Risk (Hazard Ratio [HR] and Confidence Interval) by Average Exposure (mg/m3) in Cox Proportional Hazards Regression; in Comparison HR from Cox Regression with Annually Changing Exposure Status
Relative Risk (Hazard Ratio [HR] and Confidence Interval) by Duration of Exposure (Years) in Cox Proportional Hazards Regression; in Comparison HR from Cox Regression with Annually Changing Exposure Status

Sensitivity analyses resulted in practically the same point estimates. However, case numbers were reduced and, therefore, point estimates were less precise. With Austrian citizens only the point estimate and the P value for cumulative exposure on obstructive lung diseases remained stable. All three cases had been Austrian citizens.

The results of the external comparisons are presented in Figs. 1–4. Neither for total mortality nor for the investigated causes of death an increased risk was seen in the cohort compared with the population of Tyrol.

Kaplan–Meier curves for all-cause mortality, with comparison to the population of Tyrol.
Kaplan–Meier curves for all-cancer mortality, with comparison to the population of Tyrol.
Kaplan–Meier curves for lung cancer mortality, with comparison to the population of Tyrol.
Kaplan–Meier curves for obstructive pulmonary disease mortality, with comparison to the population of Tyrol.


We did not find increased cancer risks or increased risk of lung cancer. In comparison to the general population there was a clear indication of a “healthy worker” effect and in the internal comparison there was only a weak indication of an increasing risk of death from obstructive lung disease with increasing cumulative exposure. The latter observation was based on a very small number of cases. This cohort is of relatively young age with only 177 out of 1965 persons deceased during the observation period. This renders the cohort unfit to detect very small and subtle risks. Also the exposure estimates had several weaknesses. Exposure data were missing for some departments and/or job classes. Some of these were deemed to be unexposed or with practically no exposure. However, some (usually with only few persons affected) were likely exposed and exposure had to be estimated based on comparisons with similar job classes. Exposure data were only available for the more recent time periods. A general log-linear time trend estimated from air monitoring data was confirmed by urine data, but extrapolation to earlier times is subject to some uncertainty. Earlier exposures were likely higher and also more important because of a long latency period for some of the studied outcomes. The error would likely be non-differential and would, therefore, reduce the effect estimates to the null or broaden the confidence interval thus again hiding subtle effects.

Nevertheless, the cohort was able to show the increased risk of death from obstructive pulmonary diseases albeit based on a very small number of cases. This finding is plausible23–26 but still must be treated with caution due to the small number of cases.

The within cohort models might be subject to bias by smoking behavior. It is generally known27,28 and has been shown for a subsample of the cohort that blue collar workers tend to smoke more often than white collar workers. Because blue collar workers are also generally more exposed this fact could confound the results and lead to spurious results. However, no increased risks were seen for lung cancer which would be the outcome most affected by confounding from smoking. On the whole the cohort members did not differ substantially in smoking prevalence from the general population of Tyrol and no meaningful differences in lung cancer rates were observed. Therefore, even when smoking data were incomplete it is not likely that this caused any strong confounding.

Hence, we might conclude that in this Austrian cohort exposures did not lead to very large health risks, although small risks cannot be excluded with certainty. Smoking could be a confounder because we lacked individual smoking data for a high proportion of workers and we could not link individual data on smoking behavior to cohort members. But it was shown that white collar workers (who are also less exposed on average) tended to smoke less. Therefore, any bias by smoking would have led to spuriously increased risks. Because this is why the logistic regression models that controlled for socioeconomic status (blue-/white collar workers) tended to show somewhat lower risk rates in the internal comparison. But the difference between hazard rates from Cox regression and incidence rate ratios from logistic regression were very small. The external comparison with the population of Tyrol was only done in a qualitative way. Even though there is limited evidence that smoking was somewhat more prevalent among cohort members than among the general population all mortality rates including those for lung cancer in the cohort were less than expected. This supports the null findings of the internal comparison.


The study was subject to many obstacles. Mostly these stemmed from considerations regarding data privacy protection. In previous studies29,30 we were able to collect individual mortality data through the Austrian mortality register without any problem. Detailed follow-up was also possible through local address registers in each of the Austrian districts. In special instances even social security data could be obtained. All this was no longer possible when this study was conducted. Access to the mortality register was only granted after a long campaign and many interest groups’ lobbying and an amendment of the Austrian University law. Incomplete data could not be re-checked directly because only anonymous data were provided and the Federal Statistics Institute (Statistik Austria) had been obliged to destroy the data at once after completion of their initial task. For the benefit of future research the rightful concerns for data privacy should be better balanced with rightful scientific interests.

In this cohort of hardmetal workers we did not detect increased mortality rates overall or for lung cancer compared with the general population. On the contrary all-cause mortality displayed the expected healthy worker effect. In the internal comparison none of the measures of exposure (average or cumulative exposure, duration of exposure) for cobalt was associated with increased risks for either total mortality, all cancers combined, or lung cancer.


The help of Peter Morfeld (Department of Mathematics, Ruhr-University Bochum) in the design of the study and the statistical analysis plan is gratefully acknowledged.


1. IARC. International Agency for Research on Cancer. Monographs on the Evaluation of Carcinogenic Risks to Humans. Volume 52: Chlorinated Drinking-Water; Chlorination By-Products; Some Other Halogenated Compounds; Cobalt and Cobalt Compounds. IARC 1991, Lyon. Available at: Accessed May 2016.
2. IARC. International Agency for Research on Cancer. Monographs on the Evaluation of Carcinogenic Risks to Humans. Volume 86: Cobalt in Hardmetals and Cobalt Sulfate, Gallium Arsenide, Indium Phosphide and Vanadium Pentoxide. IARC 2006, Lyon. Available at: Accessed May 2016.
3. Austrian Ministry of Labour, Social Affairs and Consumer Protection. Ordinance of the Federal Minister for Labor, Social Affairs and Consumer Protection onoccupational limit values for substances, as well as on substances with carcinogenic effects and reproductive toxicity. Available at: Accessed May 2016.
4. Lasfargues G, Wild P, Moulin JJ, et al. Lung cancer mortality in a French cohort of hard-metal workers. Am J Ind Med 1994; 26:585–595.
5. Moulin JJ, Wild P, Romazini S, et al. Lung cancer risk in hard-metal workers. Am J Epidemiol 1998; 148:241–248.
6. Wild P, Perdrix A, Romazini S, Moulin J, Pellet F. Lung cancer mortality in a site producing hardmetals. Occup Environ Med 2000; 57:568–573.
7. Hogstedt C, Alexandersson R. Mortality among hard-metal workers in Sweden. Scand J Work Environ Health 1987; 13:177–178.
8. Lison D, De Boeck M, Verougstraete V, Kirsch-Volders M. Update on the genotoxicity and carcinogenicity of cobalt compounds. Occup Environ Med 2001; 58:619–625.
9. Suh M, Thompson CM, Brorby GP, Mittal L, Proctor DM. Inhalation cancer risk assessment of cobalt metal. Regul Toxicol Pharmacol 2016; 79:74–82.
10. Armstead AL, Arena CB, Li B. Exploring the potential role of tungsten carbide cobalt (WC-Co) nanoparticle internalization in observed toxicity toward lung epithelial cells in vitro. Toxicol Appl Pharmacol 2014; 278:1–8.
11. Tanaka J, Moriyama H, Terada M, et al. An observational study of giant cell interstitial pneumonia and lung fibrosis in hardmetal lung disease. BMJ Open 2014; 27:e004407.
12. Walters GI, Robertson AS, Moore VC, Burge PS. Cobalt asthma in metalworkers from an automotive engine valve manufacturer. Occup Med (Lond) 2014; 64:358–364.
13. Kennedy K, Esmen N, Marsh G, et al. An international historical cohort study of workers in the hard-metal industry: exposure assessment. Occup Environ Med 2014; 71 (Suppl):A65.
14. Marsh G, Buchanich J, Zimmerman S, et al. An international historical cohort study of workers in the hard-metal industry: mid-study epidemiology update. Occup Environ Med 2014; 71 (Suppl):A96–A97.
15. Kennedy KJ, Esmen NA, Buchanich JM, Zimmerman S, Sleeuwenhoek AJ, Marsh GM. Mortality among hardmetal production workers: occupational exposures. J Occup Env Med 2017; 59:e297–e305.
16. Marsh GM, Buchanich JM, Zimmerman S, et al. Mortality among hardmetal production workers: pooled analysis of cohort data from an international investigation. J Occup Env Med 2017; 59:e342–e364.
17. Marsh GM, Buchanich JM, Zimmerman S, et al. Mortality among hardmetal production workers: US cohort and nested case-control studies. J Occup Env Med 2017; 59:e306–e326.
18. McElvenny DM, MacCalman LA, Sleeuwenhoek A, et al. Mortality among hardmetal production workers: UK cohort and nested case–control studies. J Occup Env Med 2017; 59:e275–e281.
19. Westberg H, Bryngelsson I-L, Marsh G, et al. Mortality among hardmetal production workers: the Swedish cohort. J Occup Env Med 2017; 59:e263–e274.
20. Morfeld P, Groß JV, Erren TC, et al. Mortality among hardmetal production workers: German historical cohort study. J Occup Env Med 2017; 59:e288–e296.
21. Hutter H-P, Wallner P, Moshammer H, Marsh G. Dust and cobalt levels in the Austrian tungsten industry: workplace and human biomonitoring data. Int J Environ Res Public Health 2016; 13:931.
22. Moshammer H, Buchanich JM, Kennedy K, Esmen N, Marsh G. An international historical cohort study of workers in the hard-metal industry-Austrian component. Occup Environ Med 2013; 70 (Suppl):A20.
23. Nemery B, Abraham JL. Hardmetal lung disease—still hard to understand. Am J Respir Crit Care Med 2007; 176:2–3.
24. Moriyama H, Kobayashi M, Takada T, et al. Two-dimensional analysis of elements and mononuclear cells in hardmetal lung disease. Am J Respir Crit Care Med 2007; 176:70–77.
25. Nemery B, Verbeken EK, Demedts M. Giant cell interstitial pneumonia (hardmetal lung disease, cobalt lung). Semin Respir Crit Care Med 2001; 22:435–447.
26. Lison D, Lauwerys R, Demedts M, et al. Experimental research into the pathogenesis of cobalt/hardmetal lung disease. Eur Respir J 1996; 9:1024–1028.
27. Lee DJ, Fleming LE, Arheart KL, et al. Smoking rate trends in U.S. occupational groups: The 1987 to 2004 National Health Interview Survey. J Occup Environ Med 2007; 49:75–81.
28. Dorner T, Fodor JG, Allichhammer D, et al. “A heart for Vienna”—the prevention program for the big city. Blue-collar workers as a special target group. Wien Med Wochenschr 2006; 156:552–557.
29. Moshammer H, Neuberger M. Lung cancer and dust exposure: Results of a prospective cohort study following 3260 workers for 50 years. Br J Occup Environ Med 2004; 61:157–162.
30. Moshammer H, Neuberger M. Lung function predicts survival in a cohort of asbestos cement workers. Int Arch Occup Environ Health 2009; 82:199–207.
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