Introduction
An ad hoc working group at the International Agency for Research on Cancer (IARC) considered dry-cleaning of textiles to entail exposures that are possibly carcinogenic to humans (Group 2B; IARC 1995a). Among these exposures, perchloroethylene (PER; also recognised as tetrachloroethylene) has been of special interest, and the substance has been upgraded from unclassifiable with regard to carcinogenic risk to humans (Group 3; IARC 1982) through possibly carcinogenic to humans (Group 2B; IARC 1987) to probably carcinogenic to humans (Group 2A; IARC 1995b). In their most recent evaluation, the IARC found consistently positive associations in studies of PER-exposed cohorts for cancer of the oesophagus, cervix and non-Hodgkin’s lymphoma (IARC 1995b). In a similar analysis, the US National Toxicology Program (NTP) also found PER “reasonably anticipated to be a human carcinogen” (NTP 2005).
Other scientific bodies have, however, adhered to more conservative risk estimates pertaining to PER. The American Conference of Governmental Industrial Hygienists (ACGIH) for instance has labelled PER an animal carcinogen of unknown human relevance (Group A3; ACGIH 2003), and an equally cautious position has been adopted by the Deutsche Forschungsgemeinschaft (DFG) (Group 3B; “a cause for concern but lack of data”; DFG 2007). In a recent critical review, Mundt et al. (2003) specifically noted the ubiquitous lack of valid exposure estimates in the epidemiological literature on PER and cancer, and they concluded that there was no epidemiological support for linking PER to cancer of any specific site. A joint Dutch-Swedish literature review found the epidemiology on PER carcinogenicity to humans inconclusive (de Raat 2003). A series of case–control studies in census-based (1970), merged cohorts of laundry and dry-cleaning workers from four Nordic countries did not yield significantly elevated risks for cancer of the oesophagus, liver, pancreas or kidney nor for non-Hodgkin’s lymphoma, whereas an excess of cancer of the cervix was not clearly related to dry-cleaning (Lynge et al. 2006). Using in part the same data base, Travier et al. (2002) found significantly raised incidence rates for Hodgkin’s disease and leukaemia (but not for non-Hodgkin’s lymphoma) in female but not in male launderers, dry-cleaners and pressers employed in the laundry, ironing or dyeing industry in both the 1960 and 1970 Swedish censuses and followed until 1989. The incidence of cervical cancer was not increased in this particular group.
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In Sweden, PER has been the quantitatively most important agent for dry-cleaning during the second half of the 20th century (Kemikalieinspektionen 1990; Johansen et al. 2005), and to assess further the potential carcinogenicity of PER, we decided to follow-up a previously assembled, national cohort of dry-cleaning and laundry workers by cross-linking with the national cancer register.
Materials and methods
As part of a Scandinavian initiative (Olsen et al. 1990), a nationwide study of pregnancy outcome in dry-cleaning workers, was undertaken in the mid-1980s (Ahlborg 1990a). A questionnaire mailed to all “washing establishments” recorded in the Swedish Postal Address Registry (n = 1,254) yielded a response rate of 37.9%. The questionnaire called for information about both the establishment (company) and the workers over a period of 11 years (1973–1983). Production volumes and washing techniques were requested as well as details of any chemicals used. No information on PER exposure at the company or individual level was available, but estimates of the proportion of PER and other detergents employed (as reported by the companies over the period of interest) were used as proxy. Names and ten-digit personal identity numbers (PINs) of the workers (Ludvigsson et al. 2009), their occupation, dates of hire and termination of employment were also requested. At least one month duration of employment was required for inclusion in the original study. All data were checked for the present study, and unidentifiable subjects or those not fulfilling original or current inclusion criteria were excluded from the analysis. Data from 14 companies were lost in the process, leaving workers from 461 companies for the study.
The size of the companies involved varied from small family businesses to establishments with several hundred employees. Each subject was assigned to one of three exposure categories based on information from the companies: the PER subgroup (genuine dry-cleaners and laundries with a proportion of dry-cleaning with PER only), the Laundry subgroup (laundries only, no PER) or Other (any combination of water, PER, chlorofluorocarbons (typically Freon 113) and sporadic cases of white spirit, naphta or trichloroethylene). Generally, data on production volumes were missing or considered unreliable but the available information indicated that most companies for which PER dry-cleaning accounted for a high proportion of their total cleaning volume (>50%) were small (cleaning <500 tonnes of textiles/year), whereas a high proportion of genuine laundries and laundries with a small PER-based dry-cleaning division were large companies (>5,000 tonnes/year). No systematic data on spot removal chemicals used in dry-cleaning shops or elsewhere were available.
In Sweden, PER has been used almost exclusively for dry-cleaning since the 1950s (Kemikalieinspektionen 1990; Johansen et al. 2005). National regulation and structural changes within the industry (reductions in demand and improvements in efficiency) have led to a dramatic (~95%) reduction in the consumption (sales) of PER from around 5,000 tonnes/year in the early 1970s to 300 tonnes/year three decades later (R Wettström, personal communication 1993; Swedish Chemicals Agency 2009). No exposure measurements of PER or other dry-cleaning agents were available from the companies in the present study, but in an exhaustive search for historical data from Nordic dry-cleaning establishments, it was concluded that PER exposure levels in the 1970s were of the order of 100–200 mg/m3 (15–30 ppm) (Johansen et al. 2005). Additional information from contemporary Swedish studies indicates that exposure to PER in the early 1980s was variable within and between various dry-cleaning establishments with the 8-h average exposure level rarely exceeding 50 ppm (Andersson et al. 1981; Lindberg and Bergman 1984; Arbetarskyddsstyrelsen 1988). In the 21st century, this remains the permissible level for occupational PER exposure for several industrialised countries (Institut für Arbeitsschutz der Deutschen Gesetzlichen Unfallversicherung 2010).
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Originally, 10,389 subjects were reported by the companies (“washing establishments”), but 677 (6.5%) were excluded for either not fulfilling the original inclusion criteria or other reasons pertaining to the present study design and 272 (2.6%) were lost in the identification process, leaving 9,440 individuals (2,810 men and 6,630 women) to follow-up (Table 1). The vital status as of 31 December 2006 of each cohort member was obtained using a PIN-based match to the national population register and the national cause-of-death register. Dates of emigration, if any, were obtained by reference to the national emigration register. Person-years were counted from 1 January 1985 until 85 years old, death, emigration or the end of the observation period, whichever came first. Emigrants returning to Sweden during the observation period were reintroduced into the study from the day of re-entry and followed up as described. For subjects with several separate episodes of employment in the industry, the total duration was obtained by summing each component period. Incident cases of malignant tumours in the cohort, coded to the 7th revision of the International Classification of Diseases (ICD-7), were obtained by matching to the national cancer register for the period 1985–2006.
Table 1
Distribution of subjects in a Swedish cohort of dry-cleaning and laundry workers
Category | Males | Females | Total |
|---|---|---|---|
Original files | 10,389 | ||
Excluded | 949 | ||
Exposure ceased before 1973 | 2 | 26 | 28 |
Exposure commenced after 1983 | 82 | 164 | 246 |
Duration of employment <1 month | 24 | 76 | 100 |
Deceased 1973–1984 (before follow-up) | 60 | 119 | 179 |
Emigrated 1973–1984 (before follow-up) | 30 | 94 | 124 |
Identity unclear | – | – | 200 |
Other | 27 | 45 | 72 |
Included (by exposure category) | 2,810 | 6,630 | 9,440 |
Dry-cleaning with PERa, % | 1,877 | 4,479 | 6,356 |
<10 | 940 | 2,466 | 3,406 |
10–50 | 412 | 854 | 1,266 |
>50 | 458 | 1,054 | 1,512 |
Unclassifiable | 67 | 105 | 172 |
Laundry | 850 | 2,051 | 2,901 |
Other dry-cleaning (fluorocarbons, white spirit) | 83 | 100 | 183 |
The outcome was compared with expected numbers of cancer derived from a computation of the person-years under observation with sex, 5 year age group, calendar year and cause-specific national rates to generate standardised incidence ratios (SIRs) for each cancer site of interest. The corresponding 95% confidence intervals (CIs) were calculated assuming a Poisson distribution of the observed events. The Statistical Package for Social Sciences (version 9.0, SPSS Inc., Chicago, Illinois) was used for organising the cohort, whereas the cohort analysis was conducted using Stata software (version 10, StataCorp LP, College Station, Texas).
The study was approved by the Uppsala Regional Ethical Review Board (decision no. 2008/007).
Results
The overall standardised cancer incidence ratio (SIR) for both genders combined was close to unity (SIR 0.96; 95% confidence interval (CI) 0.91–1.02) with a slightly more favourable outcome in women (SIR 0.91; 95% CI 0.85–0.98) than in men (SIR 1.10; 95% CI 0.99–1.23; Table 2). The findings for the female sub-cohort, which accounted for 70.3% of the entire person-time observed, were primarily due to low rates of malignant tumours of the breast, the skin and melanoma.
Table 2
Cancer morbidity 1985–2006 in a cohort of Swedish dry-cleaners and laundry workers by gender and site
Site | ICD-7 | Males | Females | Alla
| ||||||
|---|---|---|---|---|---|---|---|---|---|---|
Obs | SIR | 95% CI | Obs | SIR | 95% CI | Obs | SIR | 95% CI | ||
All | 140–209 | 337 | 1.10 | 0.99–1.23 | 769 | 0.91 | 0.85–0.98 | 1,106 | 0.96 | 0.91–1.02 |
Oesophagus | 150 | 0 | – | 0.00–0.99 | 5 | 1.33 | 0.43–3.10 | 5 | 0.67 | 0.22–1.56 |
Stomach | 151 | 16 | 1.72 | 0.99–2.80 | 18 | 1.10 | 0.65–1.75 | 34 | 1.33 | 0.92–1.86 |
Colon | 153 | 17 | 0.83 | 0.48–1.33 | 55 | 0.89 | 0.67–1.15 | 72 | 0.87 | 0.68–1.10 |
Rectum, anus | 154 | 11 | 0.77 | 0.39–1.38 | 27 | 0.85 | 0.56–1.24 | 38 | 0.83 | 0.59–1.14 |
Liver, gallbladder | 155 | 11 | 1.93 | 0.97–3.46 | 15 | 0.86 | 0.48–1.41 | 26 | 1.12 | 0.73–1.64 |
Pancreas | 157 | 10 | 1.48 | 0.71–2.72 | 24 | 1.24 | 0.79–1.84 | 34 | 1.30 | 0.90–1.81 |
Lung | 162 | 39 | 1.45 | 1.03–1.98 | 61 | 1.24 | 0.95–1.59 | 100 | 1.32 | 1.07–1.60 |
Breast | 170 | 0 | – | 0.00–7.68 | 219 | 0.88 | 0.77–1.01 | 219 | 0.88 | 0.77–1.01 |
Cervix | 171 | – | – | – | 25 | 1.25 | 0.81–1.85 | 25 | 1.25 | 0.81–1.85 |
Uterus | 172 | – | – | – | 46 | 0.92 | 0.67–1.22 | 46 | 0.92 | 0.67–1.22 |
Ovary | 175 | – | – | – | 40 | 1.03 | 0.74–1.41 | 40 | 1.03 | 0.74–1.41 |
Prostate | 177 | 82 | 0.95 | 0.76–1.18 | – | – | – | 82 | 0.95 | 0.76–1.18 |
Kidney | 180 | 10 | 1.06 | 0.51–1.94 | 19 | 1.03 | 0.62–1.60 | 29 | 1.04 | 0.69–1.49 |
Bladder | 181 | 18 | 0.86 | 0.51–1.36 | 20 | 0.98 | 0.60–1.52 | 38 | 0.92 | 0.65–1.26 |
Melanoma | 190 | 10 | 0.76 | 0.37–1.40 | 17 | 0.52 | 0.30–0.83 | 27 | 0.59 | 0.39–0.86 |
Other skin | 191 | 19 | 1.15 | 0.69–1.80 | 18 | 0.63 | 0.37–0.99 | 37 | 0.82 | 0.58–1.13 |
Brain, medulla | 193 | 9 | 0.97 | 0.44–1.83 | 27 | 1.00 | 0.66–1.45 | 36 | 0.99 | 0.69–1.37 |
Thyroid | 194 | 1 | 0.72 | 0.02–4.03 | 6 | 0.71 | 0.26–1.54 | 7 | 0.71 | 0.29–1.47 |
Other endocrine glands | 195 | 5 | 1.35 | 0.44–3.14 | 20 | 0.95 | 0.58–1.47 | 25 | 1.01 | 0.65–1.49 |
Connective tissue | 197 | 2 | 0.91 | 0.11–3.28 | 9 | 1.77 | 0.81–3.36 | 11 | 1.51 | 0.75–2.70 |
Other and unspecified | 199 | 12 | 1.31 | 0.67–2.28 | 29 | 0.92 | 0.61–1.31 | 41 | 1.00 | 0.72–1.36 |
Non-Hodgkin’s lymphoma | 200, 202 | 23 | 2.05 | 1.30–3.07 | 26 | 1.07 | 0.70–1.57 | 49 | 1.38 | 1.02–1.82 |
Hodgkin’s lymphoma | 201 | 4 | 2.88 | 0.79–7.38 | 0 | – | 0.00–1.64 | 4 | 1.10 | 0.30–2.81 |
Multiple myeloma | 203 | 3 | 0.71 | 0.15–2.09 | 8 | 0.82 | 0.36–1.62 | 11 | 0.79 | 0.39–1.41 |
Lymphoid leukaemia | 204 | 5 | 1.29 | 0.42–3.01 | 6 | 0.86 | 0.32–1.87 | 11 | 1.01 | 0.51–1.81 |
Myeloid leukaemia | 205 | 5 | 1.64 | 0.53–3.83 | 6 | 0.82 | 0.30–1.77 | 11 | 1.06 | 0.53–1.89 |
Lung cancer rates were elevated in the cohort, with an overall SIR of 1.32 (95% CI 1.07–1.60), primarily due to increased incidence of the disease in men (SIR 1.45; 95% CI 1.03–1.98). There was also a significant increase in the incidence of non-Hodgkin’s lymphoma (SIR 2.05; 95% CI 1.30–3.07) in male workers, and the point estimate was increased also for Hodgkin’s lymphoma in men, but the confidence interval was wide since only four cases were observed (SIR 2.88; 95% CI 0.79–7.38). Female workers showed no evidence of increased lymphoma risks.
Cancer of the liver and gallbladder was proportionally more common in men than in women with SIRs of 1.93 versus 0.86 (not significant) based on 11 and 15 observed cases, respectively. Cancer of the uterine cervix was observed slightly more often than expected, but this observation also did not reach statistical significance (SIR 1.25; 95% CI 0.81–1.85). No cases of cancer of the oesophagus were observed in male workers versus 3.71 expected (data not in table), whereas five cases in female workers gave an SIR of 1.33 (95% CI 0.43–3.10). Four of these cases were squamous cell carcinomas and the fifth was an adenocarcinoma. A single case of laryngeal cancer in a woman (but no male case) was observed (again not in table). For all other individual cancer sites including the kidney and the urinary bladder, overall risk estimates were within the range expected from random variation.
Further analysis indicated that the overall incidence of cancer in men was similar regardless of their category of exposure, i.e. whether they were laundry workers, exposed to PER or classified as exposed to other dry-cleaning agents (Table 3). This also applied for female workers with point estimates generally below unity. As for specific cancer sites, the excess of lung cancer was evenly distributed among the two major exposure categories for male workers, whereas among female workers, the increase was confined to laundry workers (SIR 1.63; 95% CI 1.06–2.39). There was no differential distribution of cancer of the cervix in PER-exposed or laundry workers. The incidence of malignant melanoma was low in both male and female workers within the two major exposure categories but, based on three incident cases, significantly higher than expected in men exposed to other dry-cleaning agents. The excess of non-Hodgkin’s lymphoma in male workers was of similar magnitude in both major sub-groups (PER-exposed and laundry workers).
Table 3
Cancer morbidity 1985–2006 in a cohort of Swedish dry-cleaners and laundry workers by gender, selected sites and exposure category
Site (ICD-7) | Males | Females | ||||||||||
|---|---|---|---|---|---|---|---|---|---|---|---|---|
PER | Laundry | Othera
| PER | Laundry | Othera
| |||||||
Obs | SIR (95% CI) | Obs | SIR (95% CI) | Obs | SIR (95% CI) | Obs | SIR (95% CI) | Obs | SIR (95% CI) | Obs | SIR (95% CI) | |
All (140–209) | 223 | 1.11 (0.97–1.26) | 100 | 1.08 (0.88–1.31) | 14 | 1.24 (0.68–2.06) | 501 | 0.91 (0.83–0.99) | 260 | 0.94 (0.83–1.07) | 8 | 0.48 (0.21–0.95) |
Oesophagus (150) | 0 | – (0.00–1.51) | 0 | – (0.00–3.26) | 0 | – (0.00–26.35) | 3 | 1.25 (0.26–3.65) | 2 | 1.56 (0.19–5.65) | 0 | – (0.00–46.11) |
Liver, gallbladder (155) | 8 | 2.14 (0.92–4.21) | 3 | 1.74 (0.36–5.09) | 0 | – (0.00–16.77) | 10 | 0.90 (0.43–1.65) | 4 | 0.67 (0.18–1.70) | 1 | 2.81 (0.07–15.63) |
Lung (162) | 23 | 1.30 (0.82–1.94) | 13 | 1.60 (0.85–2.74) | 3 | 2.95 (0.61–8.62) | 35 | 1.09 (0.76–1.51) | 26 | 1.63 (1.06–2.39) | 0 | – (0.00–3.55) |
Breast (170) | – | – | – | – | – | – | 140 | 0.85 (0.72–1.00) | 76 | 0.96 (0.76–1.21) | 3 | 0.63 (0.13–1.85) |
Cervix (171) | – | – | – | – | – | – | 16 | 1.19 (0.64–1.93) | 9 | 1.45 (0.66–2.75) | 1 | 1.59 (0.04–8.83) |
Melanoma (190) | 5 | 0.58 (0.19–1.34) | 2 | 0.50 (0.06–1.81) | 3 | 7.04 (1.45–20.58) | 9 | 0.41 (0.19–0.78) | 8 | 0.78 (0.34–1.53) | 0 | – (0.00–6.36) |
Other skin (191) | 14 | 1.29 (0.70–2.16) | 5 | 1.00 (0.32–2.33) | 0 | – (0.00–5.76) | 13 | 0.71 (0.38–1.22) | 5 | 0.51 (0.16–1.19) | 0 | – (0.00–6.36) |
Non-Hodgkin’s lymphoma (200, 202) | 15 | 2.02 (1.13–3.34) | 8 | 2.33 (1.01–4.59) | 0 | – (0.00–9.46) | 18 | 1.14 (0.68–1.81) | 8 | 0.99 (0.43–1.95) | 0 | – (0.00–7.53) |
Hodgkin’s lymphoma (201) | 3 | 3.22 (0.66–9.40) | 0 | – (0.00–9.00) | 1 | 23.77 (0.60–132.45) | 0 | – (0.00–2.44) | 0 | – (0.00–5.27) | 0 | – (0.00–92.22) |
While the cohort was defined as those employed in washing establishments between 1973 and 1983 and assembled in 1984, there was a built-in latency between one and 12 years at the start of follow-up in 1985. Notably, 35% of the cohort were included already in 1973 and additionally 12% before 1976. Application of a 15-year latency requirement (from 1973) therefore provided only marginally different results (data not in table).
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Using duration of employment as a proxy for duration of exposure, an inverse relationship of overall cancer incidence and duration of exposure was seen in both male PER-exposed and male laundry workers, while the incidence of liver and gallbladder cancer in men showed a tendency in the opposite direction (Table 4). For this site as well as several other less common sites, however, the number of incident cases was low and the risk estimates accordingly unstable. The excess of lymphoma cases in men was conspicuous among PER-exposed workers with the shortest exposure time, i.e. those that had more than one month but less than one year of employment during 1973–1983, yielding an SIR of 6.02 (95% CI 2.21–13.09). Among male workers with the longest duration of PER exposure (5–11 years), the incidence of non-Hodgkin’s lymphoma was slightly higher than expected (SIR 1.59; 95% CI 0.64–3.27), while among male laundry workers, the incidence of this disease was highest in those exposed for between one and four years (SIR 4.07; 95% CI 1.11–10.42).
Table 4
Cancer morbidity 1985–2006 in Swedish dry-cleaners and laundry workers by gender site, type and duration of employment
Site (ICD-7) | Duration of employment (years) | PER | Laundry | ||
|---|---|---|---|---|---|
Obs | SIR (95% CI) | Obs | SIR (95% CI) | ||
Male
| |||||
All (140–209) | <1 | 36 | 1.62 (1.13–2.24) | 18 | 1.33 (0.79–2.10) |
1–4 | 62 | 1.21 (0.92–1.55) | 27 | 1.09 (0.72–1.59) | |
5–11 | 125 | 0.98 (0.81–1.16) | 55 | 1.01 (0.76–1.32) | |
Liver, gallbladder (155) | <1 | 0 | – (0.00–9.71) | 0 | – (0.00–16.04) |
1–4 | 3 | 3.19 (0.66–9.31) | 0 | – (0.00–8.20) | |
5–11 | 5 | 2.06 (0.67–4.80) | 3 | 2.87 (0.59–8.38) | |
Non-Hodgkin’s lymphoma (200, 202) | <1 | 6 | 6.02 (2.21–13.09) | 1 | 1.68 (0.04–9.38) |
1–4 | 2 | 1.00 (0.12–3.61) | 4 | 4.07 (1.11–10.42) | |
5–11 | 7 | 1.59 (0.64–3.27) | 3 | 1.62 (0.33–4.72) | |
Female
| |||||
All (140–209) | <1 | 70 | 0.88 (0.69–1.11) | 35 | 1.06 (0.74–1.48) |
1–4 | 154 | 0.90 (0.76–1.05) | 85 | 0.99 (0.79–1.23) | |
5–11 | 277 | 0.93 (0.82–1.04) | 140 | 0.89 (0.75–1.05) | |
Liver, gallbladder (155) | <1 | 2 | 1.66 (0.20–6.01) | 1 | 1.84 (0.05–10.23) |
1–4 | 5 | 1.50 (0.49–3.50) | 0 | – (0.00–2.02) | |
5–11 | 3 | 0.46 (0.09–1.33) | 3 | 0.83 (0.17–2.41) | |
Cervix (171) | <1 | 1 | 0.32 (0.01–1.78) | 1 | 0.96 (0.02–4.81) |
1–4 | 8 | 1.72 (0.74–3.40) | 2 | 0.90 (0.11–3.24) | |
5–11 | 7 | 1.24 (0.50–2.56) | 6 | 2.13 (0.78–4.63) | |
Non-Hodgkin’s lymphoma (200, 202) | <1 | 4 | 1.95 (0.53–5.00) | 1 | 1.16 (0.03–6.48) |
1–4 | 5 | 1.04 (0.34–2.44) | 3 | 1.22 (0.25–3.57) | |
5–11 | 9 | 1.01 (0.46–1.92) | 4 | 0.84 (0.23–2.14) | |
Irrespective of category of exposure (PER-exposed or laundry employees), neither the overall incidence of cancer nor the incidence of specific cancers was positively correlated with duration of employment in women (Table 4).
As indicated in Table 3, 15 cases of non-Hodgkin’s lymphoma were observed in male workers exposed to PER and of these, eight were employees of companies for which >50% of the cleaning involved use of PER, resulting in an SIR of 3.57 (95% CI 1.54–7.04; not in table). When female workers were similarly classified, seven cases of non-Hodgkin’s lymphoma were noted (SIR 1.58; 95% CI 0.64–3.26). Some details of these individual cases, including occupational title, duration of employment, age at diagnosis and pathoanatomical classification (as recorded in the cancer register), are displayed in Table 5, but there was no clear evidence to suggest an association with PER exposure.
Table 5
Some details of non-Hodgkin’s lymphoma cases (ICD-7 200, 202) 1985–2006 employed at companies with >50% PER for dry-cleaning
Case no | Gender | Occupation | Duration of employment (years) | Age at diagnosis | ICD-7 | Morphology | SNOMEDO 10.1a
|
|---|---|---|---|---|---|---|---|
1 | Male | Dry-cleaner | <1 | 82 | 200.1 | Lymphosarcoma | NAb
|
2 | Male | Driver | <1 | 45 | 200.1 | Lymphosarcoma | CB diffuse |
3 | Male | Carpet cleaner | <1 | 55 | 202.2 | Mycosis fungoides | Mycosis fungoides |
4 | Male | Dry-cleaner | 1–4 | 60 | 200.1 | Lymphosarcoma | T-cell lymphoma |
5 | Male | Driver | 5–11 | 53 | 200.1 | Lymphosarcoma | CB/CC follicular lymphoma |
6 | Male | Dry-cleaner | 5–11 | 52 | 200.1 | Lymphosarcoma | Non-Hodgkin’s lymphoma |
7 | Male | Spot remover | 5–11 | 64 | 200.1 | Lymphosarcoma | T-cell lymphoma |
8 | Male | Foreman | 5–11 | 74 | 202.4 | Mycosis fungoides | Hairy cell leukaemia |
9 | Female | Shop clerk | <1 | 81 | 200.1 | Lymphosarcoma | CB diffuse |
10 | Female | Presser | <1 | 61 | 200.2 | Lymphoma, unspecified | NA |
11 | Female | Seamstress | 1–4 | 47 | 200.1 | Lymphosarcoma | Non-Hodgkin’s lymphoma |
12 | Female | Office clerk | 1–4 | 57 | 200.1 | Lymphosarcoma | NA |
13 | Female | Seamstress | 5–11 | 67 | 200.1 | Lymphosarcoma | NA |
14 | Female | Dry-cleaner, presser | 5–11 | 59 | 200.1 | Lymphosarcoma | CB/CC follicular and diffuse lymphoma |
15 | Female | Dry-cleaner, presser | 5–11 | 56 | 200.1 | Lymphosarcoma | Follicular non-Hodgkin’s lymphoma |
Discussion
In this historically prospective cohort study of cancer incidence in male and female dry-cleaning and laundry workers, an overall cancer incidence close to unity was observed for both genders combined. The placing of employees into discrete exposure categories allowed comparisons to be made between laundry workers who had little contact with chlorinated solvents or other toxic chemicals and dry-cleaning workers with various degrees of exposure to PER. Evidence presented here showed an increase in lung cancer in male workers without a clear association with PER exposure and a similar increase in lung cancer in female workers, which was confined to workers in genuine laundries. In addition, there was a higher than expected incidence of non-Hodgkin’s lymphoma in male workers that could not be related to PER. Overall, no specific cancer site or type was clearly associated with PER exposure in either gender.
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The present study followed over 9,400 subjects for more than two decades, making it one of the largest cohort studies of dry-cleaners and laundry workers to date apart from census-based investigations (Malker and Weiner 1984; Lynge and Thygesen 1990; Travier et al. 2002). The main strengths of the study were its prospective design with information on crude qualitative PER exposure collected before follow-up; a contrasting subgroup of laundry workers without known PER exposure; a high follow-up rate (97.2% after exclusions) based on (unique) PINs; the size of the cohort and the long follow-up period plus a valid source for data on the outcome of interest (The Swedish Cancer Register) (Barlow et al. 2009). Moreover, in parallel with the initial study and cohort ascertainment (Ahlborg 1990a), the exposure to PER was qualitatively validated by comparing data provided by the employers (used here) with information from a questionnaire to a subset of women of the cohort (Ahlborg 1990b). Using employer-based information as reference, a slight underreporting of PER exposure by the employees was observed, suggesting that the opposite situation was unlikely on a cohort basis.
Besides the obvious limited power to detect increases in rare cancer sites, this study also had some limitations with respect to assessment of occupational exposure. Firstly, no quantitative data on exposure to the compound of interest, PER, were available at either an individual or company level, so crude surrogate measures had to be used. While this approach is concordant with most other epidemiological studies of cancer in dry-cleaners (Mundt et al. 2003), it has been a consistent problem in evaluating the carcinogenicity of PER in the occupational setting. Secondly, the occupational history of the cohort members was available for a time window of only 11 years, precluding an assessment of possible confounding from occupational exposures outside this period. This could result in non-differential misclassification of subjects into the specific exposure categories used here. Moreover, historical data on PER exposure in Swedish dry-cleaning establishments suggest that exposure levels were generally low already in the 1970s and 1980s (Johansen et al. 2005; Andersson et al. 1981; Lindberg and Bergman 1984; Arbetarskyddsstyrelsen 1988), tending to reduce the power of detecting any carcinogenic risks pertaining to PER.
The so-called healthy worker effect is an example of confounding related to the observation that employed populations tend to have lower mortality or morbidity than the general population used as reference (Monson 1986; Pearce et al. 2007). This observation, however, is rarely a cause for concern in occupational cancer studies, since it is not practically feasible to take risks of future cancer development into account in pre-employment evaluations (Hernberg 1986; Thériault et al. 1994). This argument is considered applicable to the present study. The occurrence of an “unhealthy worker effect”, i.e. the increased mortality/morbidity sometimes noted in studies involving unskilled workers with short duration of employment (Juel 1994; Wingren 2006), might be considered as a mirror image of the “healthy worker effect” and more related to lifestyle-associated than strictly occupational risk factors. Some aspects of such lifestyle-related factors are discussed in the following.
The elevated incidence of lung cancer in both male and female workers observed here was not found to be confined to dry-cleaning agent exposure, suggesting alternative risk factors. An association between dry-cleaning and lung cancer has been noted previously in studies of both Scandinavian and North American dry-cleaning and/or laundry workers (IARC 1995a; Ruder et al. 2001; Blair et al. 2003) but confounding from smoking has been difficult to evaluate due to lack of data. In the present study, no data on smoking habits were available from the cohort files, but contemporary investigations at the time of cohort ascertainment provided some useful information about female workers. Unpublished data from case–control studies within the present cohort and from a complementary investigation of laundry and dry-cleaning workers (Ahlborg (1990b) indicated a prevalence of daily smoking before conception of 66–70% (data based on questionnaires from 349 subjects). These data can be compared directly to the overall rate of daily smoking of 37% in 4,687 women attending Swedish prenatal care centres in the early 1980s (Ahlborg and Bodin 1991) and to national data from the Swedish Medical Birth Register (Socialstyrelsen 2002), suggesting a considerably higher prevalence of smoking in this particular cohort when compared to other women of childbearing ages. No information on smoking habits was available for male workers, however, and any suggestion of congruence in tobacco use between genders is purely speculative.
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Since there are a high proportion of small (family) businesses in the dry-cleaning sector in Scandinavia (Lynge and Thygesen 1990), it is unclear whether the socio-economic disadvantages of US laundry and dry-cleaning workers highlighted by Blair et al. (2003) apply to Scandinavian workers. Further, in the present study, the dry-cleaners tended to be employed in smaller companies than laundry workers, suggesting differential socio-economic conditions within the textile cleaning trade. In addition, little is known about various lifestyle factors like dietary and alcohol habits in this category of (mainly) blue-collar workers. In a nested case–control study, no excessive alcohol habits were found (defined as at least 21 drinks per week) from interviews of dry-cleaners or laundry workers or their next of kin (Lynge et al. 2006), but any contrasts within the study base may have been obscured by recall bias. For the purpose of the present study, some information on alcohol habits was available from the sources indicated in the previous paragraph. Unpublished data from Ahlborg (1990b) showed that 8.7% of respondents reported alcohol habits subsequently classified as “high” (consuming beer or light wine almost daily and/or stronger alcoholic drinks at least once per week), whereas only 2.7% of the larger sample of women attending prenatal care centres were classified as “high” consumers of alcohol (Ahlborg and Bodin 1991). Since these data were collected prospectively, before the outcome here was known, they may have some credibility in suggesting an unfavourable lifestyle among the occupational groups of interest, at least in women. On the other hand, skin (squamous cell) cancer and cutaneous melanoma, both of which are strongly related to solar (ultraviolet) radiation (IARC 1992), were underrepresented in this study when compared to the general population of Sweden. Again, this observation could be taken to indicate poor socio-economic status (e.g. less availability to sun-exposed winter holidays) as much as more favourable lifestyles.
Cancer of the uterine cervix, a site repeatedly appearing in excess in previous studies of PER-exposed workers (IARC 1995b), is now understood as a disease of infectious origin (Schiffman et al. 2007) rather than associated with chemical exposures in working populations. Hence, previous observations of increased rates of cervical cancer in dry-cleaning and laundry workers are best interpreted in terms of socio-economic or lifestyle-related determinants of risk, as discussed earlier. Slightly increased point estimates of cervical cancer were observed in PER-exposed as well as laundry workers included in the present study, corroborating a concept of equal risks.
As for oesophageal cancer, another tumour site showing excess in PER-exposed groups (IARC 1995b), alcohol and smoking are well recognised and synergistic determinants, notably for squamous cell carcinoma (Lagergren et al. 2000; Morita et al. 2010). In this study, the power to evaluate the epidemiology of oesophageal cancer was low, but there was a notable gender difference. Inversely to the general background with a clear male dominance (Chandanos and Lagergren 2009), we observed a non-significant increase in female workers (both in the PER and laundry groups, respectively), whereas in male workers, no cases were observed versus 3.7 expected. These findings would suggest a differential risk panorama between the genders, but due to the low numbers involved, no conclusions can be drawn in this respect.
Non-Hodgkin’s lymphoma is a complex conglomerate of disease subtypes (Swerdlow et al. 2008), in contemporary pathology thinking including also Hodgkin’s disease (Taylor 2005) and thus creating a considerable challenge for the epidemiologist. The histological characteristics of the non-Hodgkin’s lymphomas in workers from companies using a high proportion of PER in this study (Table 5) also showed a wide variation and included both B- and T-cell lymphomas where a common aetiology is difficult to comprehend. Moreover, incident cases in this study were evenly distributed in both male and female PER-exposed and laundry workers, respectively, suggesting equal risk patterns between the groups.
Dry-cleaning with PER might well prove to represent an obsolete technology which may be replaced by a variety of environmentally “green” alternatives (so-called wet cleaning, carbon dioxide-based dry-cleaning and other methods), but the present study has not provided evidence to suggest that PER is hazardous as a human carcinogen.
In conclusion, this historically prospective cohort study of dry-cleaners and laundry workers showed no clear association between occupational exposure to PER and the subsequent incidence of cancer, adding weight to the part of the available epidemiological evidence that suggests absence of such an association.
Acknowledgments
Ing-Liss Bryngelsson provided substantial technical assistance. For the initial cohort ascertainment, financial support was obtained from the former Swedish Work Environment Fund.
Conflict of interest
The authors declare that they have no conflict of interest.
Open Access
This article is distributed under the terms of the Creative Commons Attribution Noncommercial License which permits any noncommercial use, distribution, and reproduction in any medium, provided the original author(s) and source are credited.
Open AccessThis is an open access article distributed under the terms of the Creative Commons Attribution Noncommercial License (https://creativecommons.org/licenses/by-nc/2.0), which permits any noncommercial use, distribution, and reproduction in any medium, provided the original author(s) and source are credited.