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% S' r Vinyl Chloride: Inhalation Teratology Study in Mice, Rats and Rabbits by J. A. John,* F. A. Smith* and B. A. Schwetz* These studies evaluated the effects of inhaled vinyl chloride monomer <VCM) on mouse, rat and rabbit embryonal and fetal development. Groups of pregnant CF-1 mice. Sprague-Dawley rats and New Zealand white rabbits were exposed to 500 ppm VCM for 7 hr daily during the period of major organogenesis. Subsequently, other groups of mice were similarly exposed to 50 ppm VCM, and rats and rabbits were exposed to 2500 ppm. While maternal toxicity was observed, exposure to VCM did not cause significant embryonal or fetal toxicity and was not teratogenic in any of the three species at the concentrations tested. Simultaneous exposure of some of the pregnant animals to VCM by inhalation plus 15% ethanol in the drinking water resulted in toxic effects greater than those associated with exposure to VCM alone in the three species. The fetal effects observed were similar to those reported for these three species following administration of ethanol without VCM exposure. Introduction (mice and rats) or 6-18 (rabbits) of gestation. Subsequently, additional groups of rats and rabbits Inhalation exposure to vinyl chloride monomer were exposed to 2500 ppm. For each concentration (VCM) has been shown to be carcinogenic in tested, concurrent control groups of mice, rats and laboratory animals (i, 2) and in humans (3). The rabbits were sham-exposed to filtered room air. carcinogenic potential of inhaled VCM following in Since previous studies in this laboratory indicated utero exposure has been reported (2), but observa- that the primary metabolic pathway for VCM is 4 tions to determine the teratogenic potential in blocked by ethanol (7), it was considered possible laboratory animals were not made. Epidemiologic that simultaneous administration of ethanol in the studies (4-6) of incidence rates for malformations of drinking water of animals exposed to VCM might the central nervous system among families of alter its metabolism in a manner which would employees or residents in the vicinity of vinyl enhance its toxic or teratogenic potential. Thus, in chloride polymerization facilities have not supported this experiment some of the VCM-exposed animals any evidence that VCM is teratogenic in humans. A were given 15% (v/v) ethanol in their drinking series of studies were conducted in our laboratory water during the same period of gestation. to assess the hazard associated with exposure and to investigate the mechanism by which VCM might exert its toxic effects. The purpose of the studies described in this report was to assess the embryotoxic Table 1. Teratology studies with vinyl chloride: levels of and teratogenic potential of inhaled VCM in mice, exposure. rats and rabbits. Species The exposure levels tested in the teratology VCM concn, ppm Ethanol concn, % studies are presented in Table 1. In an initial Mice 500 0 1 experiment, groups of mice, rats and rabbits were exposed to 500 ppm of VCM, 7 hr daily on days 6-15 Rats, rabbits 500 50 50 2,500 2,500 15 0 15 0 15 `Toxicology Research Laboratory, Health and Environmental Sciences USA, Dow Chemical U.S.A., Midland, Michigan 48640. Mice, rats, rabbits 500 0 0 0 October 1981 171 R&St 59910 The teratogenic potential of imbibed ethanol in mice, rats, and rabbits was previously studied in our laboratory and reported by Schwetz et al. (8). No teratogenic effects were observed when 15% ethanol was given in the drinking water to mice and rats on days 6-15 of gestation or to rabbits on days 6-18 of gestation, although retarded fetal growth and development were observed in mice and rats. Methods Female CF-1 mice (Carworth, Portage, Michi gan) weighing 25 to 30 g, Sprague-Dawley rats (Spartan Research Animals, Inc., Haslett, Michi gan) weighing approximately 250 g and New Zea land white rabbits (Langshaws Rabbitry, Augusta, Michigan) weighing 3.54.5 kg were used in this study. The day on which a vaginal plug was observed or the day on which sperm were seen in a vaginal smear was considered day zero of preg nancy for mice and rats, respectively. The day of natural mating was considered day zero for rabbits. Between daily exposures, animals were housed in wire-bottom cages in a room controlled for temper ature, humidity and light cycle. Commercial labora tory animal food (Ralston Purina Co., St. Louis, Missouri) and tap water or tap water containing ethanol were available during the periods between exposure to VCM. Food consumption was mea sured at 3-day intervals for mice and rats and at 2-day intervals for rabbits. All animals were de prived of food and water during the 7-hr exposure period each day. Exposure of bred animals was conducted in stainless steel chambers of 3.7 m3 volume under dynamic conditions. The atmosphere of VCM was generated by diluting gaseous VCM with filtered room air at a rate calculated to give the desired concentration. Vinyl chloride monomer (chloroethylene) obtained from Matheson Gas Products, Joliet, Illinois was used for the exposures. The actual concentration was measured with an infrared spec trophotometer (Perkin Elmer 12A or Miran I) with a multipath gas cell. All animals were observed daily throughout preg nancy and maternal body weights were recorded at several intervals during gestation. Pregnant mice and rats were sacrificed by carbon dioxide inhala tion on day 18 and 21 of gestation, respectively. Pregnant rabbits were sacrificed on day 29 of gestation. The uterine horns were exteriorized through a midline incision in the abdominal wall and the number and position of live, dead and resorbed fetuses were noted. After being weighed, mea sured (crown-rump length) and sexed (mice and rats), the fetuses were examined for external 172 anomalies. One-third of each litter was immediately examined for evidence of soft tissue anomalies by dissection under a low power microscope (9). The heads of those fetuses (mice and rats only) were preserved in Bouin's solution and examined for soft tissue but not skeletal anomalies (10). Rabbit fe tuses were sexed on the basis of examination of internal genitalia. All fetuses were then eviscerat ed, preserved in alcohol and subsequently cleared and stained with Alizarin Red-S for examination for skeletal anomalies (11). The Fisher exact probability test (12) was used to evaluate the incidence of resorptions among litters. Maternal and fetal body weights and body mea surements and maternal liver weights were ana lyzed statistically, by an analysis of variance and Dunnett's test (13). The incidence of fetal anomalies was analyzed by the Wilcoxon test as modified by Haseman and Hoel (U). The group of animals which was exposed only to vinyl chloride served as the control for those animals which were exposed to vinyl chloride in combination with 15% ethanol in the drinking water. The controls for animals ex posed to vinyl chloride and maintained on tap water without ethanol were exposed to filtered room air in exposure chambers which were similar to those used for exposure to vinyl chloride. Results and Discussion Maternal Toxicity Exposure to 500 ppm VCM was maternally toxic to mice; deaths (5 of 29 bred females), decreases in the amount of weight gained during gestation, in food consumption and in absolute liver weight as compared to the air only controls were observed. Evidence of toxicity was not apparent among mice exposed to 50 ppm of VCM. The combination of VCM exposure with 15% ethanol in the drinking water significantly enhanced the toxicity as com pared to VCM alone for both concentrations, though no deaths occurred in the 50 ppm VCM plus ethanol group of mice. Rats exposed to 500 ppm VCM gained less weight than controls during gestation, but no other evi dence of toxicity was observed at this level. One maternal death among 17 bred females, decreased food consumption and an increase in liver weight were observed at 2500 ppm VCM in rats. Ethanol given in combination with 2500 ppm VCM was more maternally toxic than exposure to VCM alone; the amount of body weight gained by pregnant rats during gestation and food consumption were sig nificantly decreased in the group given the combi- Environmental Health Perspectives R&S159911 nation. The liver weight relative to body weight was increased in this group as compared to the rats exposed only to VCM, but no deaths were observed as a result of treatment with the combination. An ethanol group was not included among the rats exposed to 500 ppm of VCM. Some deaths were observed among pregnant rab bits exposed to 2500 ppm VCM alone (one of seven bred females) or in combination with ethanol (3 of 19 bred females); however, other evidence of toxic ity in rabbits consisted only of decreases in food consumption among those exposed to 500 ppm VCM alone and among rabbits given the combination of 2500 ppm plus 15% ethanol in the drinking water. Among mice, rats and rabbits given 15% ethanol in the drinking water during gestation, Schwetz et al. (<S) reported that maternal toxicity, as evidenced by decreased body weights, occurred in all three species. Observations at the Time of Cesarean Section Among litters of mice exposed to 500 ppm of VCM, the incidence of resorptions was increased; 13% of the implants were resorbed versus 7% in the concurrent air controls (Table 2). Historical control data from 801 litters of CF-1 mice in our laboratory show the mean percentage ofimplantations resorbed to be 11% with a range of 6-22%. Thus, both of these values are within the range observed for control groups of this strain. Litter size and fetal body weight were decreased at 500 ppm. These effects may have been secondary to the toxicity observed among pregnant dams at this exposure level. Toxic effects on the embryo or fetus were not observed among litters of mice exposed to 50 ppm VCM. Ethanol in combination with VCM produced greater fetotoxicity than exposure to VCM alone at both levels. In the 500 ppm VCM plus ethanol group, a decrease in the percentage of pregnant mice was observed. This resulted in only seven litters, two of which contained only implantations which were re sorbed. Fetal body measurements were decreased among the ethanol groups when compared to groups given either 50 or 500 ppm VCM alone. No adverse effects on the percentage of pregnant dams or the incidence of implantations resorbed were observed among rats (Table 3). Exposure to Table 2. Mice: observations at the time of cesarean section. No VCM. no ethanol 50 ppm VCM no ethanol 15% ethanol No VCM, no ethanol 500 ppm VCM no ethanol 15% ethanol Number of litters 21 20 16 26 19 7 i Live fetuses/litter* % Implantations resorbed 10 4 15(40/261) 11 4 8(18/238) 10 4 11(19/172) 12 2 7(26/351) 11 2b 13(33/248)b 8 6' 19(13/69) Fetal body weight, g* Fetal crown-rump length, mm` 1.00 0.11 23.0 1.9 1.02 0.10 24.2 0.8b 0.84 0.14' 22.4 a: 1.5' 1.07 0.06 23.7 a 1.2 0.99 0.11b 0.78 0.15' 23.6 a 1.0 21.2 1.5' % Pregnancy 57(21/37) 74(20/27) 57(16/28) 88(28/32) 72(21/29) 31(9/29)' `Mean S.D. bSignificantly different from air-exposed control, p < 0.05. 'Significantly different from VCM-exposed group, p < 0.05. Table 3. Rats: observations at the time of cesarean section. No VCM, no ethanol 500 ppm VCM, no ethanol No VCM, no ethanol 2500 ppm VCM ------------------------------------------ No ethanol 15% ethanol Number of litters 28 Live fetuses/litter* 12 a 2 * % Implantations resorbed Fetal body weight, g* 1(4/342) 5.67 0.29 Fetal crown-rump 42.6 1.2 length, mm* % Pregnancy 96(28/29) 31 12 2 3(11/398) 5.44 0.38b 43.6 a 0.8b 94(31/33) 19 12 * 2 4(9/238) 5.59 * 0.27 43.6 1.5 95(19/20) 16 13 2 3(6/220) 5.62 a 0.29 43.3 a 1.1 100(17/17) 16 12 2 4(7/195) 5.34 0.32' 42.4 0.9' 94(16/17) `Mean S.D, hSignificantly different from air-exposed control, p < 0.05. 'Significantly different from VCM-exposed group, p < 0.05. October 1981 173 R&S159912 2500 ppm VCM plus ethanol resulted in fetal body weights and erown-rump lengths which were lower than fetal body measurements among litters from rats exposed only to 2500 ppm VCM. In the group exposed to 500 ppm of VCM alone, fetal body weights were decreased as compared to concurrent air controls, though fetal crown-rump lengths were significantly increased. In rabbits, the incidence of resorptions was significantly increased among litters given 2500 ppm VCM plus ethanol, where 53% of the implantations showed evidence of resorption versus 24% among Table 4. Rabbits: observations at the time of cesarean section. No VCM, no ethanol 500 ppm VCM, no ethanol No VCM, no ethanol 2500 ppm VCM No ethanol 15% ethanol Number of litters Live fetuses/litter1 % Implantations resorbed Fetal body weight, g* Fetal crown-rump length, mm* % Pregnancy 18 8 1 6(10/162) 35.23 4.82 91.0 4.2 100(18/18) 19 7 2b 9(14/150) 34.13 4.17 92.6 5.0 95(19/20) Mean S.D. - Significantly different from air-exposed control, p < 0.05. 'Significantly different from VCM-exposed group, p < 0.05. 11 . 63 22(19/88) 36.46 4.82 92.6 4.7 100(11/11) 5 6r4 24(10/42) 33.77 4.48 87.1 5.2 86(6/7) 16 44 53(79/149) 32.48 5.88 87.7 6.3 95(18/19) External examination Soft tissue examination Skeletal examination Bones of the skull Table 5A. Mice: incidence of fetal anomalies. No VCM, no ethanol No. fetuses (no. litters) examined 50 ppm VCM No ethanol 15% ethanol No VCM, no ethanol 500 ppm VCM " No ethanol 15% ethanol 221(20) 74(20) 221(20) 147(20) 220(20) 75(20) 220(20) 145(20) 153(14) 50(14) 153(14) 103(14) 325(26) 107(26) 325(26) 217(26) 215(19) 73(19) 215(19) 142(19) 56(5) 29(5) 56(5) 37(5) { Table 5B. Mice: incidence of fetal anomalies. No VCM, no ethanol % fetuses (% litters) affected 50 ppm VCM No ethanol 15% ethanol No VCM, no ethanol 500 ppm VCM No ethanol 15% ethanol External examination Cleft palate Anopthalmia Exencephaly Soft tissue examination Thymus Skeletal examination Skull bones, unfused Skull, delayed ossification Stemebrae, unfused Stemebrae, delayed ossification Vertebrae-lumbar spurs Vertebrae, forked atlas Vertebrae, delayed ossification 1(10) 0 0 0 0 9(35) 3(20) 7(50) 4(35) 0.4(5) 0 1(10) 0 0 0 0.7(5) 8(37) 3(25) 4(35) 5(40) 1(10) 0 2(21) 0 0 4(7) 24(50)' 40(100)* 13(57)* 44(1001* 2(21) 4(361* 1(14) 0 0 1(8) 0 1(12) 13(54) 2(19) 1(12) 4(31) 0 0 1(5) 0 1(10) 0 5(21) 3<K58)b 9(42)b 6(42)b 3(21) 0 0 6(40) 2(20) 2(26) 0 11(20) 70(100)* 34(80)* 43(100)* 14(80)* 4(20) 5(401* `Significantly different from VCM-exposed group, p < 0.05. bSignificantly different from air-exposed control, p < 0.05. 174 Environmental Health Perspectives R&S159913 those exposed only to VCM (Table 4). Only five litters were available for examination in the latter group. Litter size was decreased as compared to concurrent air controls among litters of rabbits exposed to the lower level of 500 ppm, but no effect on litter size resulted from exposure to 2500 ppm of VCM. The decreased mean litter size at 500 ppm most likely occurred because the rabbits in this group released fewer ova; the number of corpora lutea observed on the ovaries was lower among animals in this group. In the studies by Schwetz et al. (<5), a slight increase in the incidence of resorptions was ob served among litters of rabbits, but not among litters of mice or rats given 15% ethanol in their drinking water during gestation. Decreases in fetal body measurements were observed by Schwetz et al. (8) among litters from both mice and rats main tained on drinking water containing ethanol. In the present study, decreases in fetal body measure ments were more pronounced when ethanol was given in combination with VCM in these two spe cies; however it is not clear if this apparent syner gistic effect was mediated via metabolic interfer ence in the maternal animal. Incidence of Fetal Anomalies Among litters of mice, no external or soft tissue anomalies were observed at a significantly higher incidence than the respective controls for any of the exposed groups (Table 5). Cleft palate was observed in 40%, or two of the five litters examined, at 500 ppm VCM plus 15% ethanol. This incidence is not statistically increased as compared to the group exposed to 500 ppm VCM alone. Due to the low percentage of pregnancy in the females, only five litters were available for examination in the 500 ppm VCM plus ethanol group. Among litters of mice exposed to 500 ppm VCM without ethanol in the drinking water, increased incidences of three skeletal variants indicative of delayed skeletal de velopment were observed. Ethanol, when given in combination with VCM, caused a significant increase in the occurrence of a number of these skeletal variants at both levels of VCM exposure. Thus, the occurrence of delayed skeletal development coin cided with those treatment regiments which were maternally toxic and resulted in decreased fetal body measurements. .Among rats exposed to 2500 ppm of VCM, the External examination Soft tissue examination Skeletal examination Bones of the skull Table 6A. Rats; incidence of fetal anomalies. No VCM, no ethanol No. fetuses (no. litters) examined 500 ppm VCM, no ethanol No VCM, no ethanol 2500 ppm VCM No ethanol 15% ethanol 339(28) 113(28) 337(28) 225(28) 387(31) 129(31) 387(31) 259(31) 229(19) 76(19) 229(19) 153(19) 214(16) 73(16) 214(16) 141(16) 188(16) 63(16) 188(16) 125(16) Table 6B. Rats: incidence of fetal anomalies. External examination Omphalocele Soft tissue examination Microphthalmia Dilated ureter Small kidney Skeletal examination Vertebrae, lumbar spurs Vertebrae, delayed ossification No VCM. no ethanol 0 0 2(7) 0 1(4) 0.3(4) % fetuses (% litters) affected 500 ppm VCM, no ethanol No VCM, no ethanol 2500 ppm VCM No ethanol 15% ethanol T1 1(3) 0,4(5) 0 0.5(6) 00 0 2(6) 2(6) 5(10) 27(50)* 5(19)b 00 0 2(6) 9(52)b 14(68) 12(69) 35(69)b 2(16) 7(53) 4(50) 21(81)* `Significantly different from air-exposed control, p < 0.05. ''Significantly different from VCM-exposed group, p < 0.05. October 1981 175 R&SI59914 V r incidence of a single anomaly, dilated ureter was significantly higher than controls (Table 6). Ethanol did not further increase the incidence of this anoma ly. The incidence of dilated ureter was significantly lower in the ethanol group as compared to the VCM exposed group. Only minor skeletal variants were observed at an increased incidence among the ex posed rats. Lumbar spurs occurred more often than controls among litters at 500 ppm, but not among those exposed to 2500 ppm VCM alone. This vari ant was again observed at an increased incidence among the litters of rats treated with the combina tion. The incidence of delayed ossification of verte bral centra was also increased in this group and is indicative of a slight delay in skeletal development. As in mice, these skeletal changes occurred in those treatment groups where the combination of high exposure levels of VCM and ethanol produced evi dence of maternal toxicity and decreased fetal body measurements. Among rabbits, external and soft tissue anoma lies were observed at a low incidence in those groups exposed to 2500 ppm of VCM alone or in combination with ethanol (Table 7). These included a single fetus with a dilated cerebral ventricle at 2500 ppm and a single fetus with cleft palate from the group exposed to 2500 ppm plus 15% ethanol. A dilated renal pelvis was observed in two fetuses from a single litter in the latter group. Two addi tional fetuses from this group exhibited an enlarged atrium of the heart. Ossification ofthe fifth stemebra was delayed at the 500 ppm level, but not at the 2500 ppm level of exposure. Only four litters were available for examination at the 2500 ppm of VCM exposure level. These data show that the combination of VCM exposure with ethanol in the drinking water was more toxic to the developing fetus, as it was in the maternal animal, than exposure to VCM alone. However, neither treatment regimen was teratogenic in the species tested. Fetal effects consisted of increased incidences of minor skeletal variants in dicative of a delay in development in mice and rats. Similar skeletal changes (delayed ossification of stemebrae or vertebral centra and unfused stemebrae or bones of the skull) were observed by Schwetz et al. (8) in these two species given 15% ethanol in drinking water. Thus, the exposure to high concen trations of VCM in combination with ethanol in the drinking water produced toxic effects in the devel oping embryo or fetus which were similar to those produced by ethanol alone. A similar lack of teratogenicity of VCM in mice and of VCM alone or in combination with ethanol in rats was reported recently by Ungvary et al. {15). Several experiments were conducted. Exposure to 1500 ppm for 24 hr/day during organogenesis was reported to have no teratogenic or fetal effects External examination Soft tissue examination Skeletal examination Table 7A. Rabbits: incidence of fetal anomalies. No VCM, no ethanol No. fetuses (no. litters) examined 500 ppm VCM. no ethanol No VCM, no ethanol 2500 ppm VCM_______ No ethanol 15% ethanol 152(18) 50(18) 152(28) 136(18) 47(18) 136(18) 69(9) 24(9) 69(9) 32(4) 10(4) 32(4) 70(9) 25(9) 70(9) Table 7B. Rabbits: incidence of fetal anomalies. No VCM no ethanol % fetuses (% litters) affected 500 ppm VCM. No VCM, no ethanol no ethanol 2500 ppm VCM ' No ethanol 15% ethanol External examination Cleft palate Soft tissue examination Dilated renal pelvis Dilated cerebral ventricle Enlarged atrium, heart Skeletal examination Stemebrae, delayed ossification 0 0 0 0 28(77) 0 0 0 0 38(94)* 0 0 0 0 20(44) 0 0 10(25) 0 16(75) 1(11) 8(11) 0 8(11) 24(67) `Significantly different from air-exposed control, p < 0.05. 176 Environmental Health Perspectives * R&S159915 ! apart from an increase in fetal liver weight. Expo sure during the third part of pregnancy produced no deleterious effects, whereas exposure during the early days of gestation increased fetal mortality and resulted in decreased fetal body weights. Ex posure to vinyl chloride and simultaneous mainte nance on a liquid alcoholic diet during the neurulation period produced evidence of skeletal retardation, but no malformations in rats. Though the exact days of gestation during which the different treat ment regimens were employed were not stated by the author, the reported results are in apparent agreement with those from our laboratory. A report by Mirkova et al. (16) summarized the fetal and postnatal effects following exposure of pregnant rats to 6.15 mg/m3 of VCM by inhalation throughout the entire gestation period. An increase in early embryo deaths (immediately after blasto cyst implantation) and a decrease in fetal body weight were reported by these authors. Observed anomalies in the offspring included generalized he matomas, (8-fold increase over controls) internal hydrocephalus (54.5% of the fetuses), encephalocele (2.53%), and variations of stemebral ossification (2.8% of the fetuses). Several postnatal effects in dicative of hepatotoxicity and disturbances in the hepatobiliary system in the progeny following in utero exposure were also reported. The 6.15 mg/m3 level of exposure is equal to only 2.5 ppm of VCM. The exact length of exposure periods and details of the testing methods employed, especially as per tains to vapor generation and analyses, were not reported by Mirkova et al.; thus no explanation for the differences in observed effects of VCM is ap parent. The reported results are markedly incon sistent with those from our laboratory where a thousandfold increase in exposure level 2500 ppm was not embryolethal in rats, and similar fetal anomalies were not observed. In summary, exposure of pregnant mice, rats or rabbits to VCM by inhalation at concentrations sufficiently high to cause maternal toxicity was not teratogenic in any of these species. Fetal effects consisted of delayed skeletal development in mice at 500 ppm, an exposure level which was mater nally toxic, and an increase in the incidence of dilated ureter in rats following maternal exposure to 2500 ppm. In mice exposed to 500 ppm of VCM, the incidence of fetal resorptions was increased over concurrent air controls. The incidence of re sorptions observed in this group was at the high end of the range for historical control groups in our laboratory. Ingestion of 15% ethanol in the drinking water enhanced the toxicity of inhaled VCM. Fetal body measurements were decreased among mice and rats given the combination and increases in the occurrence of skeletal variants indicative of delayed development were observed in both species. The fetal effects observed were similar to those reported for these test species following administration of ethanol without VCM exposure. The incidence of resorptions was increased in rabbits given ethanol in combination with VCM, and maternal toxicity was enhanced by ingestion of ethanol in all three species. REFERENCES 1. Viola, P. L,, Bigotti, A., and Caputo, A. Oncogenic response of rat skin, lungs and bones to vinyl chloride. Cancer Res. 31: 516-519 (1971). 2. Maltoni, C. The value of predictive experimental bioassays in occupational and environmental carcinogenesis. An ex ample: vinyl chloride. Ambio 4: 18-23 (1975). 3. Creech, J. L., and Johnson, M. N. Angiosarcoma of liver in the manufacture of polyvinyl chloride. J. Occup. Med. 16; 150-151 (1974). 4. Infante, P. Oncogenic and mutagenic risks in communities with polyvinyl chloride production facilities. Ann. N.Y. Acad. Sci. 271: 49-57 (1976). 5. Edmonds, L. D., Falk, H., and Nissim, J. E. Congenital malformations and vinyl chloride. Lancet ii: 1098 (1975). 6. Edmonds, L. D., Anderson, C. E., Flynt, J. W,, Jr,, and James, L. M. Congenital central nervous system malforma tions and vinyl chloride monomer exposure: a community study. Teratology 17: 137-142 (1978). 7. Hefner, R. E., Jr., Watanabe, P, G,, and Gehring, P. J. Preliminary studies of the fate of inhaled vinyl chloride monomer in rats. Ann. N.Y. Acad. Sci. 246:135-148 (1975). 8. Schwetz, .A,, Smith, F. A., and Staples, R. E. Teratogenic potential of ethanol in mice, rats and rabbits. Teratology 18: 385-392 (1978). 9. Staples, R. E. Detection of visceral alterations in mamma lian fetuses. Teratology 9: A-37 (1974). 10. Wilson, J. G. Method for administering agents and detect ing malformations in experimental animals. In: Teratology: Principles and Techniques, J. G. Wilson and J. Warkany, Eds., University of Chicago Press, Chicago, 1965, pp. 262-277. 11. Dawson, A. B. A note on the staining of cleared specimens with Alizarin Red-S. Stain. Technol. 1: 123-124 (1926). 12. Siegel, S. Non-parametric Statistics for the Behavioral Sciences. McGraw-Hill, New York, 1956, pp. 96-104. 13. Steel, R. G. D., and Torrie, H. H. Principles and Proce dures of Statistics. McGraw-Hill, New York, 196(f, pp. 101-105, 111-112. 14. Haseman, J. K., and Hoel, D. G. Table of Gehan's generalized Wilcoxon test with fixed point sensoring. J. Statist, Comput. Simul. 3: 117-135 (1974). 15. Ungvary, G. The teratogenic effect of vinyl chloride. Munkavedelem 25: 29-33 (1979). 16. Mirkova, Y., Mikhaylova, A., and Nosko, M. Embriotoksichno i teratogenno deystviye na vinilkhloride (Embryotoxic and tetratogenic effects of vinyl chloride). Khig. Zdraveopaz. 23: 440-443 (1978). October 1981 r 177 R&SI59916