Document OEkj9zMJY36Gm0gDeayvm79ZM

to which people in the community are exposed depends on production rate, wind direction, wind velocity, and distance from the plant. In Shawinigan (population 27,000), a vinyl chloride polymerization plant (owned by B.F. Goodrich Co., Ltd.) has operated since 1943 and currently produces 25,000 tons/yr of PVC. Ten cases of angiosarcoma of the liver have been reported among workers at this plant. In addition to the PVC plant, Shawinigan has two chemical plants, one aluminum electrolysis plant, one carbide plant, and one pulp and paper mill. A great number of pollutants are discharged into its environment. Furthermora, prevailing winds tend to blow from the pollution sources towards the town's residential areas. In 1975, a high birth-defect Incidence (mostly central nervous system abnor malities) was found in three Ohio towns with PVC plants. However, two sub sequent studies failed to find any association between birth defects and either work at or proximity of residence to these plants. In a 1977 study, a higher birth-defect rate was found in Shawinigan than in Drummondville (a town without a PVC plant); the highest rates in Shawinigan were in the vicinity of the plant. The present study was an attempt to associate this high frequency of birth defects with exposure to VCM. One objective of this study was to establish birth-defect and stillbirth rates in Shawinigan and to compare these rates with those for other communities, in an attempt to confirm the high birthdefect rates previously observed. An other objective was to try to correlate seasonal and spatial variations in the birth-defect rate with variations in VCM concentration in the environment. The final objective was to compare a group of parents who gave birth to malformed infants with a control group of parents of normal children with respect to residential and occupational history and several birth-defect risk factors. In determining birth-defect rates in Shawinigan, the study included all stillbirths and malformed children born of mothers who resided within the city limits of Shawinigan at the time of delivery and who delivered between January 1. 1966, and December 31, 1979. The case-control study was limited to a shorter period (January 1973 to December 31,1979). because it required Information based on the mothers' recollection of events during their pregnancies. A birth defect was 2 defined as a gross physical or anatomic developmental anomaly present at birth or detected at the hospital during the first days after delivery. To assess the importance of the excess of birth defects in Shawinigan, three comparison communities were chosen, based on their similarity to Shawinigan in population size and structure, socioeconomic level, and medical-care facilities. To take into account the influence of environmental pollution, one town with an aluminum plant but no VCM-emitting plant (BaleComeau--Hsuterive) and two towns with neither a VCM nor an aluminum plant (Drummondville and Rlmouski) were chosen as control communities. The Quebec Population Registry provided the annual numbers of births and stillbirths in the communities; as the 1979 data were not available, numbers were estimated from the three preceding years. Birth-defect children and controls were identified and data were collected from several medical files and hospital rosters (delivery-room daybooks, birth-defect rosters, discharge lists, mothers' and children's medical files, and birth rosters). Shawinigan's 14 school districts were used as the unit of spatial distribution of birth defects. For the case-control study, the mothers of affected infants and matched controls were interviewed at home. Cases and controls were matched by maternal age within two years, sex of the Infant, and place of residence of the mother. Two studies were conducted to assess vinyl chloride concentration in the air in Shawinigan. The first was a study of the feasibility of measuring VCM in the air at several locations in Shawinigan using air sampling and analysis techniques (summarized in an appendix to the report of the present study). Its conclusion was that environ mental VCM concentrations could be assessed by ambient air sampling at various sites in Shawinigan; depending on location, sampling detected levels up to 45 oob. Ouring winter, VCM tended to accumulate in the snow inthe vicinity of the plant, and VCM concentrations t differed between indoor and outdoor 4 samples. The report recommended a continuous one-year sampling program with special attention to meteorologic, topographic, and demographic data to establish the true VCM concentrations to which the Shawinigan population is exposed. Considering the high cost of such a sampling program, it was decided that for the present study, ambient vinyl chloride concentrations In Shawinigan would be estimated using a dispersion model based on production records and the results of previous sir-monitoring activities. This study was conducted by a subcontractor. The dispersion model used the Pasquill-Gifford equation, and its variables included wind direction and velocity, rainfall, humidity, tempera ture. topography, and estimated VCM production and emissions, The model allowed construction of Isopleths of estimated vinyl chloride concentration over Shawinigan. Results From January 1966 through Decem ber 1979, there were 4534 live births and 33 stillbirths in Shawinigan. Of the live infants, 160 had birth defects, and of the stil Ibirths, 9 had birth defects. The birth defects reported most frequently were those of the musculoskeletal system, followed by the cardiovascular, central nervous, and urogenital sys tems. The ages of the mothers did not differ significantly among the various types of birth defect. Defects of the central nervous system (CNS) were particularly frequent among malformed infants with short gestation periods. The yearly numbers of malformed children per 100 births varied from 1.69 (in 1969) to 6.84 (in 1973), with an overall rate of 3.48. Detailed analysis of the month ly distribution of birth defects and the distribution by affected system for the year 1973 showed no single large increase that could account for the high rata in that year. Nor did the yearly distribution by system show any par ticular feature that could account for the annual variation in the overall rates. Furthermore, birth-defect rates did not consistently increase or decrease with time. The observed number of malformed children in Shawinigan was higher than would be expected based on the rate for each comparison community or for all three comparison communities together (see Table 1). The excess birth defects in Shawinigsn occurred In the central nervous, cardiovascular, urogenital, and musculoskeletal systems, the eye and ear, and the chest. As the types of defects found in excess in Shawinigan were also the most common types of defects overall, it can be concluded that birth defects in general were in excess in Shawinigan. The proportion of mal formed infants was greater in Shawinigan than in the comparison communities in AP00016926 Table 1. Number of Malformed Children Observed in Shawinlgan Compared with Expected Numbers Based on Rates for the Comparison Communities (1966-1979 Affected System Central nervous Cardiovascular Observed in Shawinigan 30 37 Expected Based on Drummondville 19.69* 19.69" Expected Baaed on Baie-Comeau-- Hauterive 18.18* 13.94" Expected Based on Rimouski 16.33" 43.06 Expected Based on AH Comparison Communities 17.96* 24.29* Gastrointestinal 11 9.04 9.70 10.95 9.80 Urogenital Muscuioskaietai 30 49 19.15* 36.71 13.94" 27.88" 13.14" 40.14 15.72" 34.70* Mouth and upper airways Eye and ear Chest 17 6 3 6.92" 1.06" 0.63 13.33 1.82* -- 13.14 -- 0.73 10.82 1.02" 0.41* Syndromes and other defects Total 6 JS9 6.92 102.68" 9.70 98.80" 10.95 124.08" 8.98 107.36" 'Ratio of Poisson variable to its expectation (36}: * indicates p < 0.06; ** indicates p < 0,01. all years except 1969 and 1972 (see Table 2). The number of stillbirths differed only between Shawinigan and Drummond* villa, where the number of stillbirths was significantly higher. The proportion of malformed children among the still* born was higher in Shawinigan than in the comparison communities. This is consistent with previous findings of an excess of birth defects in Shawinigan. Mothers who gave birth to malformed children were significantly younger in Shawinigan than in the comparison communities for ail malformations combined and for defects of the CMS, mouth and upper airways, and eye and ear. Children in Shawinigan did not differ from those in the comparison communities in mean gestational age at birth, except in the case of chest malformation, for whieh the sample size was very small. Figure 1 compares the monthly birth- defect rates for Shawinigan with those for Drummondville and Rimouski. The Shawinigan curve is V-shaped, with the lowest rates in the summer, whereas the curve for the comparison communi ties is flatter. The seasonal variation in birth-defeet rates was statistically significant for Shawinigan. but not for the comparison communities. The spatial distribution of birth defects in Shawinigan with respect to the PVC plant was analyzed: In no Table 2. Distribution of Malformed Children for Each Year (1966 1979) Year Shawinigan Rata* 1966 1967 1968 1969 1970 1971 1972 1973 1974 1975 1976 1977 1978 1979 Total 16 13 8 6 IS 6 6 18 8 15 13 14 11 10 159 3.54 3.52 2.30 1.68 4.70 2.08 2.19 6.84 2.97 4.40 3.98 4.56 3.33 3.11 3.48 Number of malformed children per 100 births. * indicates p < 0.05. Comparison Communities 31 33 24 27 24 30 34 44 43 51 36 50 52 47 526 Rates 1.82 1.96 1.51 1.78 1.66 2.05 2.43 3.17 2.81 3.10 2.20 2.76 2.88 2.69 2.35 SH/Comparison Communities'" ;,55* 1.80 1.52 0.94 2.83 1.01 0.90 2.16* 1.06 1.42 1.81 1.66 1.16 1.16 1.48* 95% Confidence interval (1.08. 3.52) iO.bS. 3.39) (0.69. 3.34) (0.41. 2.18) (1.65,5.17) (0.53, 1.94) (0.36. 2.20) (1.28. 3.65) (0.48, 2.33) (0.81, 2.49) (0.93, 3.51) (0.93, 2.93) (0.61, 2.20) (0.60, 2.26) (1.24, 1.75) 3 APOOOt 6927 previous abortions. There was one pievious stillbirth among the control mothers and none for the case mothers; there was one previous malformed child in each of the two groups. Thera was no significant difference between cases and controls in the lather's age. No mother (esse or control) was exposed to X-rays during the first trimester of pregnancy, and only one case mother was exposed during the second third of pregnancy; exposure during the third trimester did not differ significantly between case and control mothers. Table 4 summarizes the mothers' occupations before and during their pregnancies. None of the women were ever exposed to VCM at work before or during pregnancy. The working experi ences of the case and control mothers before and during pregnancy did not differ, nor did their smoking habits or alcohol consumption. Two mothers of Month of Birth defective infants reported having used the drug LSD before their pregnancies. figure 1. Monthly distribution of birth-defect rates. There was no significant difference between cases and controls in the father's occupational exposure to school district did the ratio of observed to expected number of birth defects differ significantly from 1, The four not differ significantly, nor was there a significant difference between case and control mothers in number of previous chemicals, and no fathers were ever exposed to vinyl chloride (see Table 5). The distance between each mother's districts with the highest rates ere pregnancies. place of residence and the VCM plant located on the north-south axis passing Mothers of malformed infants reported was measured to 100 m, using a map through the vinyl chloride plant; the no excess of diseases during pregnancy; of the city; there was no significant district In which the plant is located had about the expected number of birth however, the following diseases sus pected to bear a high risk of birth defect difference between the two groups in distance from the VCM plant. defects. The yearly average concentra tion of vinyl chloride was estimated for were reported more frequently by case than by control mothers: rubella, Discussion each school district, based on data from hydramnios, epilepsy, nonpsychotle Some observations of this study s study entitled "Dispersion Patterns of mental disorders, and psychosis. There support the existence of an association Vinyl Chloride Emitted by B.F. Goodrich Co.. Ltd.. Shawinlgan, Que." (which is was no significant difference between case and control mothers in number of between VCM in the air and birth defects in the exposed community, appended to the report of the present study). Birth-defect rates did not differ between school districts with high and low VCM exposure, either for all birth Table 3. Comparison of Total Birth Defects1 and CNS Birth Defects* Between School Districts with High and Low Atmospheric Vinyl Chloride Concentration defects or for CNS defects (see Table 3). Likewise, school districts adjacent to the plant did not differ from the other school districts in numbers of birth defects (total or CNS), nor did districts Births with defects School Districts With High VCM Levelsa 87 School Districts With Low VCM Levels 70 Total m differ within and beyond a one-mile radius of the vinyl chloride plant. For the period January 1973 to Births without defects 2286 2126 4410 December 1979, 68 cases of birth defects were Identified in Shawinigan Births with CNS defects 16 13 29 and matched with controls (42 male and 26 female pairs). Five of the cases were stillborn; all of the controls were born Births without CNS defects 2356 2182 4539 alive. There was no significant difference between cases and controls in number of weeks' gestation at delivery. The Total births 'X\ - 0.80: p> 0.35. 2372 2136 4567 frequencies of previous birth defects in y,a o.io: p> 0.70. the families of cases and controls did cSchool districts nos. 1, 3, 5, 6. 7, and 8. 4 APOOO16928 Table 4. Distribution of Cases and Controls by Mother's Occupation1 Mother's Occupation Cases Before During Pregnancy Pregnancy Control Before During Pregnancy Pregnancy Work outside home without exposure ro chemicals 41 22 42 20 Work in VCM industry 0 0 0 0 Work outside home with exposure to chemicals 2 1 2 1 Stay at home Total 25 45 24 47 68 68 63 68 Partitioning stay at home vs. work outside home before pregnancy: X*, = 0.03; p > 0.85. Partitioning stay at home vs. work outsidehome duringpregnancy: X2i -0.13;p >0.71. while others tend to contradict such an association. High birth-defect rates in Shawinigan were confirmed for a 15year period, and women who gave birth to malformed children were, on average, younger in Shawinigan than in the comparison communities. These results are consistent with previous findings for three Ohio towns with PVC plants. The present study revealed seasonal variation in birth-defect rates that could correspond to variation in atmospheric VCM concentrations. VCM could not be measured in air samples during Decem ber, January, and February. It is believed that during these months, VCM tends to accumulate near the plant as a liquid, because the outdoor temperature is below its liquefaction point; this VCM would be released into the air in the Spring. Birth-defect rateswere lowest in September, which is eight months after midwinter, corresponding to the time between the first third of pregnancy and delivery. This observation would tend to support an association between VCM concentration in the air and birth defects in the community. One con sultant believed that below its liquefac tion point VCM would remain in the air in droplets, at a concentration similar to that found at higher temperatures. However, because people spend more time indoors during the winter than the rest of the year, winter exposure would tend to be low in any case. On the other hand, several observa tions of the present study tend to argue against any association between VCM concentration in the air and birth defects in the community. The spatial distribution of birth defects in Shawinigan cannot be explained on the basis of estimates of VCM concentrations in the community. Malformation rates were not relatively high either near the plant or in the area where VCM concentrations were estimated to be highest, and the school district with the highest birth- defect rate was far from the plant. However, VCM concentrations were not measured directly, but estimated by a theoretical dispersion model based on approximate production and emission values, because the B.F. Goodrich Co. would not release the actual values. Table 5. Distribution of Cases and Controls by Father's Occupation* Father's Occupation____________________Cases Ever worked in vinyl chloride industry 0 Controls 0 Ever worked in industries with exposure to chemicals Never worked in industries with exposure to chemicals Unknown Total 20 43 5 68 25 39 4 68 X*, = 0.73; p> 0.33. There was no difference in occupa tional or residential history between the parents who gave birth to malformed infants and the control parents. Both groups resided at similar distances from the plant and none of the parents had worked at the plant Furthermore, all types of birth defects were in excess in Shawinigan, rather than those of any particular system. These results agree with those for the three Ohio cities; however, egents known to be teratogenic in humans and experimental animals have very specific effects, and it seems unlikely that any agent would produce the variety of malformations found in excess in Shawinigan. Possible explanations of the results as artifactual are not convincing. It is unlikely that Shawinigan's physicians were'more inclined to diagnose birth defects than were physicians in the comparison communities. Birth defects were included in this study on the basis of their obviousness, and the birthdefect rates were the same in the three comparison communities. Furthermore, for severe birth defects like those of the CNS. which cannot be misdiagnosed, rates were much higher in Shawinigan than in any of the comparison com munities. The method bywhich the data were col lected made it very uni Ikely that a bias in the quality of the information from the archives of the regional hospitals could have influenced the results. The possibility remains that pregnant mothers residing outside of Shawinigan who were at risk of having a malformed child migrated to the city for delivery, thereby increasing the birth-defect rate for that town. In the case-control study, 9ix mothers (6.7%| were rejected because they had moved to the city of Shawinigan after the first third of pregnancy, and four more cases were untraceable. Thus, as many as 11% of the birth-defect cases observed in Shawinigan. might actually have come from elsewhere, reducing the number of observed cases to 142. However, birth-defect rates would still be sig nificantly higher than in the comparison communities, leading us to believe that the excess noted in Shawinigan was real. Animal atudies have shown that exposure to high levels of VCM during pregnancy results more often in high rates of fetal loss and miscarriage than in birth defects. However, stillbirth rates were no higher in Shawinigan than in the comparison communities, and in the 5 APOOO16929 casa-control study, abortion rates were not higher for case than for control mothers. Several industries in Shawinigan emit pollutants into the atmosphere, and several of the pollutants may interact to generate potent mutagenic or teratogenic chemicals in the com* munity, The analysis of such an envi ronment and its association with the excess of birth defects was beyond the scope of the present study. However, in the case-control study, there was no difference between the numbers of case and control parents who worked at the aluminum plant, and the comparison community with an aluminum elec trolysis plant (Bate-Comeau--Hauterive) had lower birth-defect rates than did Shawinigan. Thus, the aluminum in dustry probably was not solely respon sible for the excess of birth defects in Shawinigan. Among risk factors (other than occu pational or environmental exposure to a pollutant) known to be associated with birth defects, epilepsy and mental disorders before and during pregnancy and the use of the drug LSD before pregnancy were reported more fre quently by mothers of malformed children than by control mothers. Drugs prescribed to control epilepsy have been reported to be associated with birth defects and could accountfor afewbirth defects observed in Shawinigan, as could LSD. No other risk factor was reported more frequently by the case than by the control mothers. An association between VCM in the air and birth defects in the exposed community cannot be substantiated at the present time. If the association exists, it cannot be measured by the methods used in this and in previous studies or in populations of the sizes studied so far. Conclusions The conclusions of this study can be summarized as follows: 1. For the years 1968 through 1979, there was an excess of birth defects in the population of Shawinigan, Quebec. This result is similar to the findings for several U.S. cities where vinyl polymerization plants operate. 2. Birth-defect rates underwent a seasonal variation that could cor respond to variation In the con centration of VCM in ambient air. 3. Mothers from Shawinigan who gave birth to malformed infants 6 were younger than mothers from the comparison communities who also gave birth to malformed intents. 4. The excess malformations involved not only the central nervous system, but almost all body sys tems. 5. No correlation was found between the spatial distribution of birth defects in the town and estimates of VCM concentrations in the air. (These estimates were based on approximate data, since informa tion on PVC production and VCM emissions was not available.) 6. Occupational exposure as a causal agent was ruled out. because none of the parents in the study harfavsr worked at t ha VCM ala nt. 7. Cases and controls did not differ in distance of residence from the plant. ' 3. No .excess of stillbirths was ob- served in snawmigan, and abortion rates were no higher for mothers of malformed Infants than for mothers of normal infants. Some observations of this study support an association between VCM in the air and birth defects in the exposed community, while others tend to indi cate that no such association exists. As the present results are inconclusive, the possibility that VCM generates birth defects in human communities requires further consideration. This would best be accomplished through a program during the next five to ten years to monitor VCM concentration in the air and birth defects in the exposed communities. Gilfes P. Theriault. Hildafturra, and Suzanne Gingras are with the Department of Social and Preventive Medicine, Faculty of Medicine. Lava/ University. Ste-Foy, Quebec. Canada G1K 7P4. Jeff Beaubiar and Gregg Wilkinson are the SPA Project Officers (see belowJ. The complete report, entitled "Association Between Birth Defects andExposure to Ambient Vinyl Chloride, " (Order No. PB B t -238 883: Cost: Pit .00, subject to change) will be available only from: National Technical Information Service 5285 Port Royal Road Springfield, VA 22161 Telephoner 703-487-4650 The SPA Project Officers can be contacted et: Health Effects Research Laboratory U.S. Environmental Protection Agency Research Triangle Park, NC 27711 A U S. GOVERNMENT PRINTING OFFIC& t981 - 757 012 7327 AP00016930