Document KRyxnEJM2NXYrbaq4n9ard3e0

American Journal of Industrial Medicine 17:553-565 (1990) Mortality and Cancer Morbidity in Workers Exposed to Low Levels of Vinyl Chloride Monomer at a Polyvinyl Chloride Processing Plant .ars Hagmar, md, Bengt Akesson, bsc, Jerri Nielsen, md, Christina Andersson, BSc, Katarina Linden, bsc, Robyn Attewell, MSc, and Torgil Moller, md To study whether exposure to low levels of vinyl chloride monomer (VCM) causes increased risk for cancer morbidity and death from ischemic hean disease, a cohort study was performed among 2.031 male workers ai a polyvinyl chloride (PV'C) processing plan; who had been employed for at least 3 months during the penod 1945-1980. An almost significant!)' increased total mortality (SMR -- 116. 959c Cl 99-136) was found. Deaths caused by violence or intoxication were significantly increased (SMR = 153. 959c Cl 109-213). but not deaths from ischemic hean disease (SMR = 100. 959c Cl 73-135;. A significant increase in total cancer morbidity was observed (SMR = 12S. 959- Cl 101-161). Respiratory cancers were significantly increased (SMR = 213. 959 Cl 127-346). Furthermore, six brain tumors (vs. 2.6 expected) were observed. This increase, however, was not significant (SMR = 229, 959 Cl 8^-498). No liver hemangiosarcoma was observed. Applying a latency period of ^10 years from Stan of employmen; did not change the risk patterns There were no significant exposureresponse associations between exposure estimates for VCM. asbestos, and plasticizers and cancer morbiditv. words: asbestos, brain cancer, plasticizers, phthalic acid esters, respiratory cancer, ischemic heart disease INTRODUCTION It is weli-established that vinyl chloride monomer (VCM) may induce angio sarcoma of the liver, but there have also been suggestions of increased risks for lung cancer [Buffler et al., 1979; Waxweiler et al., 1976]. brain tumors [Beaumont and Breslow. 1981; Cooper. 1981]. melanoma [Storetvedt Heldaas et al.. 1984], and nematopoietic malignancies [Weber et al.. 1981] in workers producing VCM or polyvinyl chloride (PVC). The exposure levels for VCM had, however, been very high in the latter workplaces. In contrast, the exposure to VCM has been substantially Depanmeni of Occupational Medicine. University Hospital. Lund. Sweden (L.H., B.A.. J.N., C.A.. K.L.. R.A ) Regional Tumor Registry. University Hospital. Lund. Sweden (T.M ) Address reprint requests to Dr. Lars Hagmar. Department of Occupational Medicine, University Hospital. 5-22i 85 Lund, Sweden. -..'Cepied for pubiicauon November 28. 1989 1990 Wiley-Liss, Inc. VC6146 fili H tii'i:-i-: i r?i I i` l t-:l UK fKe- 554 Uagmar et al. lower in the PVC processing industry. No excess cancer mortality or morbidity was observed in a Swedish cohon study of employees from four PVC processing plants [Molina et al., 1981]. On the other hand, a proportionate mortality study of employ ees in PVC fabricators showed an excess in total cancer mortality, particular.1 that of the digestive system [Chiazze et al.. 1977]. Thus, whether low-level exposure to VCM increases the cancer incidence is not known. However, it should be remem bered that there also has been exposure to other carcinogens, such as asbestos and certain plasticizers, in those working in the PVC processing industry'. A much used plasticizer, di(2-ethylhexyl)phthalate (DEHP), has been regarded as carcinogenic in mice and rats by the lARC [1982]. An increased mortality due to myocardial infarction w'as observed in the pre vious Swedish cohon study of PVC-processing workers, which, hypothetically, was ascribed to a damaging effect on the blood vessels by VCM [Molina et al.. 1981]. We repon here on mortality and cancer morbidity in a cohon of workers from a PVC processing plant in which PVC. after addition of various chemicals, is heat-treated for fabrication into floor and wall coverings, pipes, sheets, and food packaging. The present plant is one of the four included in the previous Swedish cohon study [Molina et al., 1981]. As we have extended both the inclusion and observation period for the study and also obtained information from previously neglected company records, fewer than 509c of the subjects in the present cohon were included in the previous study. One aim of the present study was to investigate whether there was an increased risk for cancer among employees in the PVC processing industry' and whether such risks could be associated with specific chemical exposures. Funhermore. it was regarded as imponant to clarify whether there was an increased mortality from my ocardial infarction or other cardiov ascular diseases. SUBJECTS AND METHODS The Plant The plant was founded in 1945. Initially, both the production and the number of employees were limited, but. since the mid 1950s. the production has been more extensive. The three main products manufactured in the plant are the following. 1) Thick film floor sheeting, floor tiles, and homogenous mats, have been produced since 1947 in calenders from PVC containing phthalic acid esters, mainly DEHP. as plasticizers. Asbestos, mainly chrvsotile. used as reinforcer, was added to the PVC in the mixing department until 1977. 2) Thin film has, since 1952, been calendered from PVC, containing mostly DEHP, diisodecyl phthalate. and butylbenzylphthalate as plasticizers. The film was cut into diapers or ribbons for mat production or ex ported in rolls for use as packing material. 3) Pipes have, during the period 19521975, been extruded from PVC. containing mainly DEHP as a plasticizer. Further more, lead and cadmium compounds have been added as stabilizers. Exposure Estimates For each calendar year 1945-1980, each work operation in the plant has been classified by an occupational hygienist in cooperation with technical and safety stall of the plant, with regard to the estimated mean exposure levels of VCM. asbestos, VC6147 Mortality and Cancer at a PVC Processing Plant 555 and plasticizers, A four-grade scale, "none," "low," "moderate," or "high" ex posure level, was used. The exposure to VCM was rather stable until 1975, when the exposure levels rapidly decreased due to the first repons of the association with liver hemangiosarcoma. Before 1975. the mean exposure level among "highly" exposed workers (workers in the mixing departments and calender operators) was estimated to be about 10 ppm. among "moderately" exposed workers (e.g., machine anendams) about 1 ppm. and among workers exposed to "low" levels of VCM (quality inspectors and .acking personal) about 0.1 ppm. Based on this information, the individual cumu lated exposure (ppm-years) was calculated by adding the exposure estimates for each calendar year. The cumulated exposure data were used in dose-response calculations. The estimates for asbestos were partly based on measurements of breathing zone levels. In 1971. the mean exposure level among "highly" exposed workers (raw material transport workers, workers in the mixing departments and PVC crushing, and calender operators) was 1-3 fibers/ml. among "moderately" exposed workers (machine attendants and repairmen) >0.1-0.5 fibers/ml, and among workers ex posed to "low" levels of asbestos (quality inspectors and packing personnel) uptoO. 1 "bers/ml. Measurements were performed over a total of 108 hr. No measurements of asbestos were performed before 1971, but. based on the best available judgements, the time-weighted average exposure levels after 1969 were estimated to have been about 409c lower than those in the period 1956-1969. Air sampling in 1975 indicated that the mean exposure level in all exposed workplaces had decreased by a factor of 3 compared to the period 1970-1974. No asbestos was used in the manufacture after 1977. The individual cumulated exposure for asbestos (fiber-years/ml) was calcu lated. in the same manner as for VCM. by adding the exposure estimates for each calendar year. The exposure levels for plasticizers were stable during the whole study period, .'ne time-weighted average breathing zone level of phthalic acid esters among "highly" exposed workers (calender operators) was >0.5--3 mg/m', among "mod erately" exposed workers (workers in the mixing departments and machine atten dants) >0.1-0.5 mg'nv, and among workers exposed to "low" levels of VCM (quality inspectors and packing personnel) up to 0.1 mgrinC The individual cumulated exposure for plasticizers (mg-vears) was calculated, in the same manner as for VCM and asbestos, by addins the exposure estimates for each calendar-year. Cohort From the company's records, name, date of birth, address, and dates of start and end of employment were obtained for 2.043 male workers who had been employed for 3 months or more during the period 1945 to December 31, 1980 (Fig. 1). The records, however, contained no data on workers who had left employment or died before 1961. Vital status was determined up to December 31, 1985 (Table I) for all but 11 subjects (0.5%), whose ten-digit personal identification code could not be estab lished. Six of these subjects had been employed for less than 1 vear. If a 10 year ..uency period was used, the total loss in follow-up was 0.7%. Thus the study cohort consisted of 2,031 subjects. Table 11 shows the distribution of person-years by age group and calendar year. VC6148 Living Dead Emigrated Not identified3 Total 1.726 159 146 11 2.042 84.5 7.8 7.1 0.5 100.0 *A ten-digit personal identification code could not be established. 1.536 108 19 11 1.674 TABLE II. Person-Years of Observation in a Cohort of 2,031 Workers in a PVC Processing Plant Calendar year 1961-1970 1971-1980 1981-1985 Total <30 2,334 5,753 1,366 9,453 Age (years) 30-59 60-79 2,624 9,140 6,418 IS.182 290 1.224 1.001 2,515 91.8 6.5 1.1 0.7 100.0 Total 5,248 16.117 8.785 30,150 Y* 3 .v Information on Causes of Death and Tumors Information on cause of death (1961-1985) was obtained from the National Swedish Central Bureau of Statistics. The death certificates were coded according to the International Classification of Diseases (ICD) by the National Swedish Central ^ VC6X49 dence respo duraf VCM perso progT expo; subje itv of ciatio negat corre; expo; 1198- cance are g; The t SMR RES: Mort Mortality and Cancer at a PVC Processing Plant 557 Bureau of Statistics, which is responsible for the coding of all Swedish death certif icates. All codes were transformed to the Eighth Revision of the 1CD. Death certif icates regarding causes of death of special interest were obtained. A total of 50% of the death certificates were based on clinical or forensic autopsy in subjects who had died before 80 years of age. If the 10 year latency period was used, the figure was 49%. Information on up to two tumors (coded according to the 1CD. Seventh Revi sion) diagnosed from 1961 to 1985 was obtained from the National Swedish and the Southern Swedish Regional Tumor Registries. Case records from hospital as well as autopsies were scrutinized. Risk Estimates The person-year accumulation in the cohort started in 1961. Date of death, emigration or 80th birthday were used as individual endpoints. With regard to cancer morbidity, date of diagnosis of 2 second tumor was also used as an individual endpoint. Expected mortality for the period 1961-1985 was calculated using calendar ear-, cause-, and 5 year age group-specific mortality rates for males in the county tBlekinge; about 75,000 male inhabitants). These rates were calculated from death and population counts obtained from the National Central Bureau of Statistics. Sim ilarly. yearly morbidity rates for cancer in the period 1961-3985 for the county were obtained from the Southern Swedish Regional Tumor Register. Cause-specific standardized mortality/morbidity ratios (SMRs) and 95% confi dence intervals (Cl) were calculated according to the Poisson distribution. Exposureresponse relationships were assessed by analyses of SMRs over strata, based on duration of employment and the individual total cumulated exposure estimates for "CM, asbestos, and plasticizers [Bresiow et al.. 1985]. Each individual contributes person-years successively to each employment and exposure estimate stratum as he progresses through his employment time [Swaen and V'olovics. 1987], Thus, the exposure-response relationships were based on classified person-years and not on subjects. The correlation between age and length of employment affects the comparabil ity of the SMRs from each employment stratum. Furthermore, there is also an asso ciation between the cumulated exposure estimates and age. This may result in a negative bias in the SMRs. especially for those employed for a long time. Thus, to correct for the relationship between age and length of employment or cumulated exposure, an aee-standardized SMR (SSMR) was calculated accordins to Ranstam [1984]. To clarify possible interactive effects of the three different chemical agents on cancer incidence, the distribution of subjects, observed number of tumors, and SMRs are given for the eight combinations of ever being exposed (or not) to the three agents. The term "significant" refers tops 0.05 or to the lower limit of the 95%- Cl for SMR 5: 1.00. AH tests are two-tailed. RESULTS Mortality During the period 1961-1985, 156 deaths were observed vs. 134.6 expected (SMR = 316, 95% Cl 99-136; Table III). The cumulated number of deaths in the VC61S0 m 4l Ml ?- ? - 558 Hagmar et al. TABLE HI. Observed (0) and Expected fE) Mortality 1961-1985 and Specific Causes of Death in a Cohort of Workers in a PVC Processing Plant" Cause of death Organ Malignant tumors Gastrointestinal tumors Respiratory tumors Cardiovascular diseases Ischemic bean diseases Bronchms. emphysema, asthma Gastrointestinal diseases Urinary tract diseases Violence. intoxication AJ) C4U&S Al!" Ten years latency-period*' 1CD-S O E SMR 95<* Cl O E SMR 95C! 140-209 3 30.8 J22 88-17) 29 20.7 140 95-203 150-159 14 10.7 131 72-220 11 7.6 145 72-260 160-163 10 6.6 153 73-280 6 4.6 130 48-284 390-458 60 60.1 410-4M 44 44.0 490-4S3 4 2.0 520-577 7 4.6 100 77-129 47 43.5 100 73-135 36 32.3 201 55-514 3 1.3 15! 61-312 3 2.7 108 Si-*-!4f 111 79-156 v"17 47-665 112 23-328 580-599 4 1.4 291 79-745 3 0.8 389 80-1140 800-999 37 24.2 153 109-213 16 10.6 151 Sv-250 000-999 156 134.6 116 99-136 105 86.5 121 100-147 *5MR. standardized mortality ratio, "2.031 subjects. 30.150 person-years under observation. bl.663 subjects, 12.1 S3 person-years under observation. jab: Work Sue cohort is plotted with regard to time in Figure I. With regard to cause-specific mortality, there was no significantly increased risk of death in malignant tumors (SMR = 122 . 95% Cl 88-17]). cardiovascular diseases (SMR = 100. 959c Cl 77-129). or ischemic heart diseases (SMR = 100, 959c Cl 73-129: Table III). Four deaths from obstructive lung diseases, vs. two expected, were observed. However, this was far from statistically significant (SMR = 201. 959c Cl 55-514). On the other hand, deaths from violence or intoxication were sianificamly increased (SMR = 153. 95% Cl 109-213). When a latency-period of & 10 years was applied. 105 deaths were observed vs. 86.5 expected (SMR = 121.95% Cl 100-147). The pattern of cause-specific deaths was not affected by the applied latency period. Cancer Morbidity A significant increase in total cancer morbidity was observed (SMR = 128, 95% Cl 101-161; Table IV). The cumulated number of tumors in the cohort is plotted with respect to time in Figure 1. Among the specific cancers, there was a significant increase in respiratory cancer (SMR = 213, 95% Cl 127-346), consisting of an increased incidence of both laryngeal cancer (SMR = 391, 95% Cl 81-1140.) and lung cancer, including one case of mesothelioma (SMR = 186, 95% Cl 99-3)8;' Table IV). The increased incidence of brain tumors did not reach a statistically significant level (SMR = 220. 95% Cl 84-498). Of the six observed brain tumors, : '***'.^ Dose incide 2=10 } signif. and in to asb cers (. statist There c..;im: } been c percer incide from t exposi (SMR *7 in the cancer subjec VC6151 Mortality and Cancer at a PVC Processing Plant 559 : ABLE IV. Observed fO) and Expected (E) Tumor Morbidity 1961-1985 in a Cohort of Workers in a PVC Processing Plant* Tumor Sire Gastrointestinal tract Liver, bile ducts Respirators tract Nose, sinuses Larynx Lung, pleura . estate Brain All 1CD-7 O E 150-158 155 160-164 160 161 162-164 177 193.0 140-209 19 14.9 m n" 1.1 17 8.0 ~r 0.2 3 0.8 13 7.0 11 6.5 6 2.6 TT 58.6 Alt' SMR 127 189 213 448 391 186 170 229 128 9519 C) 78-202 23-684 !2'-346 11-2500 81-114 99-318 85-304 84-498 101-161 fcTtn years latency-period'' O E SMR 959; Cl 14 10.6 2 0.8 n 5.6 i 0.1 3 0.6 7 5.0 10 5.2 A 1.6 55 39.8 133 244 195 803 549 141 191 258 138 70-213 30-880 97-349 20-4470 113-1610 57-290 91-351 70-660 105-181 *SMR. standardized mortality ratio. '2.051 subjects. 30.150 person-years under observation. ''1.663 subjects. 12.18? person-years under observation five were astrogliomas and one a meningeoma. Neither of the two liver tumors `served was a hemangiosarcoma. When a latency period of 2: 10 years was applied, the total cancer morbidity was of the same magnitude as without the latency period (SMR = J38. 959c Cl 105-181; Table IV). The morbidity from respiratory cancer was still about doubled (SMR = 195, 959c Cl 97-349), but the excess risk for lung and pleural cancer had decreased somewhat (SMR = 141. 959c Cl 57-290). On the other hand, the increased inci dence of laryngeal cancer reached statistical significance (SMR * 549. 959c Cl 113-1610).' Dose-Response Analysis There were no significant associations between length of employment and the incidence of respiratory cancers or total cancer incidence, regardless of whether a 200 years latency period was applied or not (Table V). Furthermore, there were no significant associations between the individual cumulated exposure estimates to VCM and incidence of respiratory or total cancer (Table VI). "High" cumulated exposure to asbestos (a3.3 fiber-years/ml) was significantly associated with respiratory can cers (SSMR = 295, p * 0.01). but the exposure-response relationships were not statistically significant for either these tumors or total cancer incidence (Table VII). There were no significant associations between the individual cumulated exposure estimates to plasticizers and incidence of respiratory or total cancer (Table VIII). None of the subjects in the cohort had been exposed to VCM only. 289c had been exposed to asbestos only, and 69o to plasticizers only (Table IX). Thirty-four percent of the cohort had been exposed to all three agents, but no increased cancer incidence was observed for this subcohort. However, the case of mesothelioma was from this category. Fourteen percent of the cohort had not been exposed to any of the exposure agents. The total cancer incidence was. however, increased in this group (SMR = 183. 959c Cl 100-308). Finally, a total of 189c of the cohort were classified w the remaining three exposure combinations. A significant increase for respiratory' cancer (SMR = 1070. 959c Cl 220-3120) was observed in the subcohon of 76 subjects exposed to both asbestos and plasticizers but not to VCM. 560 Hagmar el al. TABLE V. Relationship Between Time of Employment and Risk of Cancer Morbidity* Time of employment (years) TABLE Cancer Tumor < 1 tmean 0.5)' 1-5 (mean 2.4)* >5 (mean 12.3)* Sue 1CD-7 O SMR SSMR O SMR SSMR O SMR SSMR P Respiratory tract 160-164 3 295 295 3 254 252 5 J45 138 0.2S Sue n- Lung, pleura 162-164 -3 221 221 1 96 109 4 133 132 >0.5 Respirat, I Al! 140-209 12 155 155 12 139 145 3! 132 123 >0.5 Lung. All *A latency penod of 10 years has been applied. The calculations were based on 1.663 subjects. 0. observed cases. SMR. standardized morbidity ratio. SSMR. SMR standardized to the age distribution m "A laten. the <1 year group. P for trend in SSMR. observed *3.579 person-years at risk ihe <0.0 **3.553 person-years at risk. *5,057 person-years at risk. j3.885 pc ''4.386 pc 3.S75 pe TABLE VI. Relationship Between the Cumulative Exposure Estimates for Vinyl Chloride Monomer fVCM) and Risk of Cancer Morbidity* Cumulative exposure estimates (ppm-vears) table \ Risk of c Tumor <0.1 (mean 0.02lJ 0.1--1 (mean 0 4)* >1 (mean 23r Site 1CD-7 O SMR SSMR O SMR SSMR O SMR SSMR P Respiratory tract 160-164 6 247 247 n 161 109 3 153 165 >0.5 Sue Lung, pleura 162-16J 5 232 00 0 2 116 123 >0.5 Respirator All 140-209 26 14? 149 14 155 14S 15 112 105 0.3 Lunc. p The calculations were based on 3.658 subjects. A latency period of 10 years has been applied O. All f- observed cases: SMR. standardized morbidity ratio. SSMR. SMR standardized to the age distribution in "A latent;, the <0,1 ppm-vears category: p for trend in SSMR. obsen. ed c "5,543 pernm-years at risk, the <0.05 t3.542 person-years at risk. j4,64J per *3,062 person-years at risk. i'5.662 per '5.S5S per> DISCUSSION The main result of the present study is an increased incidence of total cancer morbidity, and more specifically of respiratory cancers, in PVC processing workers. Validity No preemployment health examination was performed before 1968, when the company founded its medical health service. Even after that, there has been no focus on cardiovascular or respiratory diseases in preemployment health examinations. There is not likely to have been any self-selection against employment in the plant, but this possible bias can of course not fully be excluded. Thus there is no reason to believe that there has been any significant bias in selection of employees into the cohort affecting mortality from cardiovascular or chronic obstructive respiratory dis eases. However, it is possible that workers with such diseases may have left work selectively, causing an underestimation of risk. Since 1968, the employees have been examined routinely by chest X-ray even' 5 years: no tumor has yet been diagnosed by this means. No other screening test for cancer has been performed among the workers. Thus there is no reason to believe that rumors h populatic Dia conclusic cohort. 5 which is county (a for cause: region. T caused ar diagnosec Smc cancer. T that the r. industrial `ban in tb for respir: VC6153 Mortality and Cancer at a PVC Processing Plant 561 TABLE VII. Relationship Between the Cumulative Exposure Estimates for Asbestos and Risk of Cancer Morbidity* Cumulative exposure estimate (fiber-yearvml) Tumor Site 1CD-T Respiratory tract Lung, pleura All 160-164 162-16-1 140-209 <0.03 (mean 0.002)"' 0.03-3.3 (mean 1.2)" >3 .3 (mean 13.5'1, O SMR SSMR O SMR SSMR O SMR SSMR 3 162 2 121 22 16S 162 1 73 121 0 0 168 |4 137 51 7 290 0 5 255 140 19 (16 295 241 112 P 0.18 0.14 0.29 "A latency period of fclO years has been applied. The calculations were based on 1.658 subjects. 0. observed cases: SMR. standardized rporbidits ratio: SSMR. SMR standardized to the ase distribution in the <0.03 fiber-years'ml category: P for trend in SSMR "3.885 person-years at riskb~ .386 person-years at nsk l3.8"5 person-vears at risk. TABLE VIII. Relationship Between the Cumulative Exposure Estimates for Plasticizers and Risk of Cancer Morbidity* Tumor Sue ICD-7 Respiratory tract 160-164 Lunj. pleura '162-164 All 140-209 Cumulative exposure esumate (mg-years) <0.05 (mean O.CUb 0.05 -0.5 (mean 0.3)h >0.5 (mean 2r O SMR SSMR O SMR SSMR O SMR SSMR 1 52 1 58 19 135 52 5 3"3 58 168 135 15 15? 334 5 213 158 4 194 142 21 132 204 138 P >0.5 >0.5 >0.5 "A latency period of ElO years has been applied. The calculations were based on 1.65S subjects. O. observed cases: SMR, standardized morbidity ratio; SSMR. SMR standardized to the age distribution in the <0.05 me-years category; p for trend in SSMR. - .6+4 person-years at risk - .663 person-years at nsk. "5.858 person-years at risk. tumors have been diagnosed earlier in the exposed cohort than in the reference population. Diagnostic accuracy for causes of death, as well as tumors, is important for the conclusions. Information on cause of death could be obtained for all deceased. In the cohort. 505c of the death certificates were based on clinical or forensic autopsy. - .itch is somewhat higher than the frequency of autopsy in deceased males in the county (about 36%), Thus, there are reasons to believe that the diagnostic accuracy for causes of death in the cohort is somewhat better than average in this geographical region. The somewhat increased autopsy rate in the cohort does not seem to have caused any bias with respect to tumor diagnosis; e.g.. no case of lung cancer was diagnosed by autopsy only. Smoking is a potential confounding factor for both lung cancer and laryngeal cancer. The smoking habits in the cohort are not known. However, it is not unlikely fhai the number of smokers in the cohort, as well as in other groups of Swedish k'fustrial workers [Hagmar et ah. 1986; Socialstyrelsen, 1986]. are somewhat higher lnan the reference population. This may explain some of the observed excess risk for respiratory cancer. The exposure estimates were only partially based on measure- VC6154 m m 4Hui;.lI -Hi iliac! m i IS k 562 Hagmar et al. TABLE IX. Relationship Between Cancer Morbidity and the Eight Combinations of the Three of death ir. w Exposures virtually never exposed; -r, exposed) for 1.660 Subjects; Vinyl Chloride (VCM), Asbestos, and Platicizers* men in Su I! respect to t All cancer Respirator)1 cancer groups thai PlasticizersAsbestosAsbestos - Plasticizers -1AsbestosAsbestos -i- VCMN O SMR 227 472 99 76' 14 5 3 4 183* 79 180 193 VCM-r N 0 SMR 00 70 214 5 565 24 0 0 131 133 VCMO SMR VCMO SMR 1 105 0 0 00 I 4S7 0 3 1.070* 2 0 0 0 88 Cancer Me The g which is in fabricators ? other hand. PVC proces partly of the *A latency period of a 10 years has been applied standardized morbidity ratio. *95% Cl 100-308. *95% Cl 220-5.120. N, number of subjects; 0. observed cases; SMR. now availab The in increase whi does not sire in the preser ments and were mainly based on skilled, but subjective, assessments of exposure levels. Thus, the individual cumulated exposure estimates we used are. as in most retrospective cohort studies, rather crude. any specific power for e: relatively fe\ risk for respi Mortality reach forma, chrysotile-in. In many cohort studies among industrial workers, no increased overall mortality- chrysotile ha ratio is found. This has usually been ascribed to a "healthy worker effect" [Mc- workers wen Michael. 1976]. On the other hand, we have, in two recent studies of workers in the was 13.5 fib; chemical industry, observed increased overall mortality ratios compared with regional should be ex; reference populations [Hagmar et ah, 1986: Englander et al.. 1988]. The almost sure of 17.2 f significantly increased overall mortality in the present study is in accordance with to date of dia those findings. A major cause of the overall increase is the 50% excess in violent Asbestc deaths or intoxications. This was also observed in our previous studies on workers in Peto. 1985], the chemical industry [Hagmar et al., 1986; Englander et al.. 1988], The observed study, but thi excess risk is probably correlated with socioeconomic factors, including alcohol abuse. No increased incidence of deaths from cardiovascular diseases, or more spe these subjects exposure io ; obvious. cifically from ischemic heart diseases, was observed in the cohort. This is in contrast It is alsc to a previous Swedish study on the PVC processing industry, including a part of the VCM exposur present cohort, in which a slight excess risk for myocardial infarction was indicated these tumors [Molina et a)., 1981], but is in concordance with the results of a proportionate formally signi mortality study among employees of PVC fabricators [Chiazze et a!., 1977], Fur had ever beer thermore, the incidence of ischemic heart disease was not increased in previous studies on workers producing VCM or PVC, who were exposed to much higher levels of VCM [Doll, 1988]. processing ph Maltoni et al. One aim Four subjects in the cohort died from chronic obstructive respiratory diseases could be asso; compared with two expected. The numbers are still too small to allow any interpre significant dos tation. It should be remembered, however, that only a few studies on occupational ciation betwee groups have shown increased mortality in chronic obstructive respiratory diseases. It served. Severe has been shown that men who are not gainfully employed had a highly increased risk sociations are VC6155 Mortality and Cancer at a PVC Processing Plant 563 of death in chronic obstructive respiratory diseases compared to gainfully employed men tn Sweden [Jarvholm et al.. 1988]. Therefore, it has been proposed that, with respect to these diseases, other occupational groups constitute more suitable reference groups than the general population [Jarvholm et al.. 1988], Cancer Morbidity The present study showed an increased incidence of total cancer morbidity. which is in agreement with a proponionate mortality study among employees of PVC fabricators showing an excess of total cancer mortality [Chiazze et al.. 1977). On the ther hand, such an increase was not observed in a previous Swedish cohort study on ?VC processing workers [Molina et al.. 1981]. However, the present study consists partly of the same subjects as in this latter study. but a longer follow-up period was nov> available. The increase in respiratory tumors was significant. However, the SMR did not increase when applying a 10 years latency period from start of employment, which does not strengthen the hypothesis of a causal association with the work environment m the present plant. Furthermore, no clear-cut exposure-response associations with any specific chemical agent could be established. On the other hand, the statistical oower for exposure-response associations with specific tumor sites was limited by elatively few expected cases. Thus, the association between exposure to asbestos and risk for respiratory tumors, indicated in Table Vll. is noteworthy, even if it does not reach formal significance. According to Doll and Peto [1985], the incidence of chrysotile-induced lung cancer increases with 19c per fiber-years/m!. Mainly chrysotile had been handled in the present plant, and the exposure levels for most workers were relatively low (mean exposure level in the "highly'' exposed stratum was 13.5 fiber-vears.-ml). Therefore, no dramatic effects with regard to lung cancer should be expected. The subject with mesothelioma had a cumulated asbestos expo sure of 17.2 fiber-years/m! and had a 36 year latency period from first day of exposure o date of diagnosis. A causa) association is therefore probable in this case. Asbestos exposure is regarded as one of the causes of laryngeal cancer [Doll and Peto. 1985]. A significant increase in that diagnosis was observed in the present study, but this was based on only three cases. The cumulated asbestos estimates for these subjects were no; impressive; 6.8, 5.1. and 1.3 fiber-years/ml. Thus, whether exposure to asbestos contributed to the increased risk for laryngeal cancer is not obvious. It is also noteworthy with regard to previously suggested associations between VCM exposure and brain tumors [Beaumont and Breslow. 1981] that the incidence of these tumors was more than doubled in our study, even if ihe increase was not formally significant. On the other hand, only three of the six cases of brain tumors had ever been exposed to VCM. In previous case reports, VCM exposure in PVC processing plants has been associated with hepatic angiosarcomas [Wagoner. 1983; Maltoni et al.. 1984]. No such tumors were observed in our study, however. One aim of our study was to test whether the increased cancer risks in the cohort could be associated with exposure to VCM. asbestos, or plasticizers. However, no significant dose-response associations were found, even if a tendency towards asso ciation between respiratory cancers and cumulated exposure for asbestos was ob served. Several explanations for this inability to demonstrate exposure-response as sociations are possible. The observed excess risks may be due to nonidemified. VC61S6 564 Hagmar et al. nonoccupational confounding factors or may be attributable to more complicated exposure interactions between chemical agents in the plant, which cannot be analyzed with our methodological approach. Alternatively, the lack of observed dose-response associations may be due to weaknesses in the applied, rather crude, exposure esti mates. Furthermore, the statistical power for detecting significant exposure-response associations between chemical agents and specific tumor sites was limited in the present study by few expected cases. A follow-up study with more person-years under observation will provide an increased precision, which should clarify the risk pattern connected with employment in the PVC processing industry. ACKNOWLEDGMENTS This project was supported by grants from the Swedish Work Environment Fund, the Swedish Cancer Society, and from Ellen. Walter, and Lennart Hesselman's Foundation for Scientific Research. Dr. T. Ax. Prof. B. Holmberg, and Mr. W, Jakobsen are gratefully acknowledged for their valuable assistance. Sociably: Storetved: pol Swaen G.\ tor Wagoner J PerWaxweiler wot Weber H. exp, REFERENCES Beaumont JJ. Breslow N (1981). Power considerations in epidemiologic studies of vinyl chloride workers. Am J Epidemiol 114:725-734. Breslow N'E. Lubm JH. Marek P. Langholz B (1983): Multiplicative models and cohort analysis. J Am Slat Assoc 78:1-12. Buffler PA. Wood S. Eifler C, Suarez L. Kilian DJ (1979): Mortaliiy experience of workers in a vinyl chlonde monomer production plant. J Occup Med 23:195-203. Chiazze L. Nichols WE. Wong O (1977)- Mortahtv among emplovees of PVC fabricators. J Occup Med 19:623-628. 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