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IARC MONOGRAPHS VOLUME 19
2.3 Analysis
No Information was available to the Working Croup on methods for determining PVC realduea in foods or ot^ier parts of the environment.
A rapid and simple way of identifying fifteen packaging films,,includ ing PVC, has been described in which the films were treated with ten dif ferent solvents and the solubility and physical appearance of the film at room temperature and at the boiling-pointa of the solvents were'noted (Van Gieson, 1969).
Plastics, including PVC, have been identified by measurement of the pH of an aqueous solution of the pyrolysis products, followed by thin-layer chromatography, and by reaction of PVC with pyridine (Braun A Nlxdorf, 1972).
PVC has bean separated from plasticizers, stabilizers, modifiers, fillers, pigments and other inorganic additives by gel permeation chroma tography or sequential solvent extraction. The resulting additive-free fraction has been analysed by chlorine analysis, infra-red spectroscopy, molecular-weight determination by viscosity measurements and thermal gravimetry and differential thermal analysis (Brookman, 1974).
Pyrolysis-gas chromatography has been proposed to identify PVC in polymers used In medical applications (Nematollahi et al.t 1970), in three commercial polymers (In this case, pyrolysla-gaa chromatography was used in combination with tbemogravlnetrlc analysis and differential thermal analysis) (Boettner et at-* 1969), and among some chlorine-containing polymers (Tsuge et alt 1969). Pyrolysis-gas chromatography has also been used to identify polymers, including PVC, among 37 coBerclal polymers (Olouaoto & Takeuchl, 1972), in plastics and rubbers (Fischer, 1967) and in adhesives used in building (in this case, pyrolysla-gaa chromatography was used in combination with thermogravimetry, differential thermogravlnetry and differential thermal analysis) (Rons, 1971).
Thin-layer chromatography of pyrolysis products has been used to iden tify high polymers. Including PVC (Pastuska, 1969).
Thermogravlmetry and infra-red spectral analysis have been used to determine PVC in floor tiles (Powell, 1974).
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VINTL CHLORIDE AND POLYf-tRS
409
/ 3. Biological Data Relevant to the Evaluation of Carcinogenic Risk to Humans
3.1 Carcinogenicity studies in animals1
~
Subcutaneous or intraperltoneal administration
Rat: A group of 45 adult Ulster rate were given s.c. Implants in the abdomlnsl wall of squares or discs of a commercial PVC known to contain some additives; the Implants were 0.04 m> thick and 15 am wide. At the appeararee of the first tumour, 44 animals were still alive. Seventeen (38.6X) malignant tumours (fibrosarcomas and 1 llposarcoma) developed at the site of film implantation, with a latent period of 189-727 days; s similar but perforated film did not produce local tumours In 27 rats at risk. No local tumours were found In s group of 50 rats given s s.c. implant of cotton (Oppenhelmer et dl., 1952, 1955). With a pure PVC film of 0.03 mm thickness, 4 malignant ttmoura were obtained after 533 days in a similar group (Oppenhelmer et al., 1955) (The Working Group noted that the reporting of this experiment was preliminary and that final results wars never forthcoming].
Groups of 35 (male and female) Wistar rata were given a s.c. implant
Into the abdomen of PVC film 4 x 5 x 0.16
A group of 25 control rata
received an Implant of glass of similar size. After 300 days, 30 and 20
animals were still alive in the two groups, respectively; all surviving
rats were killed 800 days after Implantation. One sarcoma and one fibroma
were found after 580 days in the PVC-treated rata, whereas no local tumours
developed in the control group (Ruasell et al,t 1959).
A group of 80 outbred albino rats (sex unspecified) received implants (of unstated size) of PVC film by laparotomy to surround the kidney. The
animals were sacrificed at 3, 10, 15, 30, 90, 195, 285, 300 and 380 days after the Implantation. Of rats that survived 285-375 days, 6/16 developed fibrosarcomas st the site of Implantation (R-ilkhlln A Kogan, 1961).
In rats Implanted In the kidney with ei:her PVC capsules, whole PVC films or perforated PVC films, 5/16, 2/5 and 1/5 sarcomas ware observed (Kogan A Tugarinova, 1959).
*The Working Group was aware of a study in progress to assess the carcinogenicity of PVC powder by inhalation exposure and intrapleural administration to rats (IARC, 1978s).
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I ARC MONOGRAPHS; VOLUME 19
3.2 Other relevant biological data
(a) Experimental systems
Bats and guinea-pigs exposed continuously to PVC dust for 24 hours/
day for periods varying from 2-7 months were found to have extensive Lung damage (Frongla et al., 1974).
The growth of granulation tissue around PVC particles Impllnted into the muscles of rabbits has been reported (Guess & Stetson, 1968). Severe fibroblastic reactions were found in rats (Calnan, 1963) and dogs (Harrison et al., 1957) which received PVC sponge implants into the a.c. tissue of the anterior abdoelnal well.
Ingested and rectally absorbed PVC particles (5-110 ym) were found to
be transported by both the lymphatic and the portal system from the intes tinal wall of rats, guinea-pigs, rabbits, chickens, dogs and pigs (Volkheimer, 1975).
In rats, inhalation of fusee from heated PVC produced interstitial
oedema, as well as focal bronchial and intra-alveolar haemorrhage in the lungs of some animals (Cornish & Abar, 1969).
No data on the embryotoxicity, teratogenicity, metabolism or muta genicity of this compound were available to the Working Group.
(b) Humans
Workers exposed to PVC dust during the manufacture of articles made from PVC showed alterations in the respiratory organa (e.g., changed bron-
chovascular pattern, increased pulmonary ventilation at rest) (Vertkln & Mamontov, 1970).
Pneumoconiosis due to inhalation of PVC dust was suggested following pulmonary biopsies In a male patient who had Inhaled PVC dust for 1 year and exhibited granulomatous lesions due to foreign bodies. The severity of the disease was shown by the observed dyspnoea, secondary polyglobulia and reduced respiratory function (Szende et at., 1970).
Fibrotic lung changes and altered pulmonary function tests have been reported in 96 workers exposed to PVC dust; the changes were more pro nounced in those with long exposure (Lllls et al., 1976; Waxveller et al., 1976).
Reduced pulmonary function and an enhancement of pulmonary function defects associated with an increased risk of respiratory Impairment were
noted in a number of nonsmoking workers exposed to an occupational environ
ment contaminated with vinyl chloride fumes and PVC dust (Miller, 1975; Miller et al., 1975).
VINYL CHLORIDE *4) POLYMERS
411
In 15 polyvinyl production workers employed in 'PVC-processing indus tries' , where stabilizers, colours and bulk materials were added to and mixed with the basic PVC powder, the following pathological findings were reported: in 7, slight to moderate thrombocytopenia; In 7, increased bromosulphaleln retention; in 6, reticulocytosis; in 1, leucopenla; and in 1, alight splenomegaly. Neither scleroderma-like ekln changes nor Raynaud's syndrome were observed (Lange et al., 1975). A large proportion of abnormal liver function tests and platelet counts were found in a group of 37 PVC process workers: 202 had abnormal alkaline phosphatase, 60S abnormal lactic dehydrogenase, 302 abnormal serum glutamic-oxaloacetic transaminase, 102 abnormal serum glutamic-pyruvic transaminase, and 352 abnormal platelets (Wegman, 1975).
Casea of 'meat-wrappers* asthma* have been reported. In which neat wrappers developed respiratory symptoms when exposed to fumes of PVC film sealed and cut with a hot wire. The identity of the causative agent(s) has not been established (Brooks ft Vandervort, 1977; Falk ft Portnoy, 1976; Polakoff et al., 1975; Sokol et al., 1973).
During tha period 1970-1975, 175 fire-fighters experienced respiratory distress due to the toxicity of hydrogen chloride gas released from the combustion of PVC plastics (Dyer ft Each, 1976). Carbon monoxide, hydro chloric acid and phosgene (Cornish ft Abar, 1969; Dyer ft Each, 1976) have been reported as the major PVC pyrolysis products of toxicological Impor tance, although more than 75 components have been identified following the thermal degradation of PVC (Dyer ft Each, 1976).
The few esses of dermatitis that have been reported ere believed to be caused by sensitivity to plasticizers in polyvinyl plastics (Morris, 1953).
3.3 Case reports and epid<M*ologlcal studies1
A proportional mortality study was carried out using death certifi cates from 1970-1972 of 707 male plastic workers (extruding, moulding, cutting, turning or otherwise machining plastics, and Including PVC fabri cating). A statistically significant excess of stomach cancer mortality was found (24 observed vereue 16.4 expected, P<0.05) (Baxter ft Fox, 1976) TThe study Is limited by the use of proportionate mortality methodology and by the fact that not all deaths studied were among workers engaged in acti
vities directly involving PVC].
*The Working Group was aware of a study in progress on workers exposed to PVC (IAR.C, 1978c).
412
I ARC MONOGRAPHS VOLIME 19
In a cross-sectional mortality study of 4341 deaths during 1964-1973 among current and former employees of 17 PVC fabricators, an excess In total cancer mortality, particularly that of the digestive system, was reported among both white males and vhltte females. The risk of cancer of the breast and urinary organs was also qeported to be In excess among white females (Chlazze et al., 1977) [The study Is limited by the use of proportionate mortality methodology and by the fact that not all deaths were among workers engaged In activities directly involving PVC]
Casterline et al. (1977) reported a case of a 22-year-old male who developed a squamous-cell carcinoma of the buccal mucosa as a result of a habit, acquired at the age of 8 years, of chewing plastic materials con taining PVC. No prior history of mouth or lip lesions, of smoking tobacco or drinking alcohol, or of occupational exposure to vinyl chloride was noted.
Vinyl chloride-vinyl acetate copolymers
1. Chemical and Physical Data
1.1 Synonyms and trade "w-es
Chem. Abstr. Services Reg. No.: 9003-22-9
Chen. Abstr. Name: Acetic acid ethenyl ester polymer with chloroethene
Acetic add vinyl ester polymer with chloroethylene; chloroethylenevinyl acetate polymer; polyvinyl chloride-polyvinyl acetate; vinyl acetate-vinyl chloride copolymer; vinyl acetate-vinyl chloride polymer; vinyl chloride-vinyl acetate polymer
A 15; A 15 (polymer); A 15-0; A 15S; Bakelite LP 70; Bakelite VLFV; Bakelite VMCC; Bakelite VSJD 10; Bakelite VYHD; Bakelite VYHH; Bakelite VYNS; Bakelite VYNW; Breon 351; Breon 425; Breon AS 60/41; Corvlc 51/83; Corvlc 236581; Corvic R 46/88} Deakalac 41M; Denka Vinyl m 90; Diamond Shamrock 744; Diamond Shamrock 7401 Exon 450; Exon 454; Exon 470; Exon 481; Exon 760; Flovic; Geon 100x150; Geon 130x10; Geon 135; Geon 351; Geon 400x47; Geon 421; Geon 427; Geon 434; Geon 103EP-J; Geon 440L2; Geon 450xl50PN; Geon 150XML; Geon 103ZX; Hostallt PVP; Leucovyl PA 1302; Lucovyl GA 8502; lucovyl MA 6028; lucovyl PA 1208; Marvinol VP 56; 50ME;
VINYL CHLORIDE AND POLYMERS
413
Norvlnyl P 6; Opalon 400; Pevikon C 870; Pllovac A0; Pllovic AO;
PVC Cordo; Reain 4301; Rhodopas 6000; Rhodopas AX; Rhodopas
AX 30/10; Rhodopas AX 85/15; Sarplfan HP 1; Solvic 523KC; Solvlc
PA 513; Solvlc 513PB; Sumllit PCX; Tennua 0565; VA 3 (copolymer);
VAGD; VH 10/60; Vilit 40; Vlnnol H 10/60; Vlnnol H 15/45; Vinnol
H 40/60; Vinylite VGHH; Vinyllte VYDR; Vinyllte VYDR 21; Vinyllte
VYFS; Vinyllte VYHD; Vinylite VYHH; Vinylite VYNS; Vinylite VYNW;
Vinyon; VLVF; VMCC; VYHH; VYNS; VYNW
1,2 Structural and molecular formulae and molecular weight
In combination with
HH
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Mol. wt: -100 000
1.3 Chemical and physical properties of the cc polymers
(a) Description: White powder
(b) Stability: Sensitive to excessive exposure to heat and light in the absence of added stabilisers. Hydrogen chloride gee la a decomposition product of degradation.
1.4 Technical products and Impurities
Low levels of vinyl acetate are copolymerized with vinyl chloride to obtain realns with specific properties. Depending upon the use, the vinyl acetate level may vary from 2-20Z, with an average of 11-12Z. As described in the monograph on polyvinyl chloride, p. 405, various additi ves are used to aid in processing the resins.
No detailed information on the possible presence of unreacted monomers In the copolymers was available to the Working Group.
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I ARC MONOGRAPHS VOLUME 19
Studies which Indicate increased rates of birth defects among the children of parents residing in communities where vinyl chloride production and polymerization plants are located indicate the necessity for further investigation of the teratogenicity oA vinyl chloride and Its polymers In
both animals and humans.
The available studies on polyvinyl chloride, which indicate an elevated proportion of digestive system cancer in male and female workers and possibly of cancers of the breast and urinary organs in female workers involved In the fabrication of plastics, Including polyvinyl chloride, are insufficient to evaluate the carcinogenicity of thle compound.
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VINYL CHLORIDE AND POLYMERS 5. References
419
Anderson, D., Hodge, ll.C.E. & Purchase, I.F.H. (1976) Vinyl chloride: dominant lethal studies in male OJ-1 mice. Hitat. Rea.. 40, 359-370
Anderson, D., Hodge, M.C.E. & Purchase, I.F.H. (1977) Dominant lethal studies with the halogenated olefine vinyl chloride and vlnylldene dichloride in male CD-I mice. Environ. Health Perspect.. 21, 71-78
Andrews, A.W., Zawlstowski, E.S. 6 Valentine, C.R. (1976) A comparison of the mutagenic properties of vinyl chloride and methyl chloride. ttutat. Res.. 40, 273-276
Anghelescu, F., Otolu, M., Dobrlnescu, E., Hsgl-Psraschlv-Dosslos, L., Dobrlnescu, G. 4 Ganea, V. (1969) Cllnlco-pathogenlc considerations on Raynaud's phenomenon In the employees of the polyvinyl chloride industry (Rom.). Med. interna (Buc.) , 21, 473-482
Anon. (1972) Fire Protection Guide on Hazardous Materials, 4th ed., Boston, Maas., National Fire Protection Association, pp. 325M-137, 49-226-49-227
Anon. (1973a) 'Prior sanction' regulation proposed for PVC. Food Chemical Mews, 21 May, p. 42
Anon. (1973b) FDA to propose ban on use of PVC for liquor use. Food Chemical Have, 14 May, pp. 3-4
Anon. (1974) CIA argues case against zero VCM exposure limits. Eur. Chemical Neve. 24 May, P* 24
Antweller, K. (1976) Studies on the metabolism of vinyl chloride. Environ. Health Perspect.. 17, 217-219
Bsrbin, A., Brisil, H., Croisy, A., Jacqulgnon, P.f Malavellle, C., Montesano, R. A Bartsch, H. (1975) Liver-sicrosome-mediated formation of alkylating agents from vinyl bromide and vinyl chloride. Blorhsm. blophya. Res. Cwmi., 67, 596-603
Baretta, E.D., Stewart, R.D. 4 Mutchler, J.E. (1969) Monitoring exposures to vinyl chloride vapor: breath analysis and continuous air sampling. An. ind. Hyg. Assoc. J., 30, 537-544
Barnhart, W.L., Toney, C.R. A Devlin, J.B. (1975) Environmental/Industrial Hygiene Surveys of Vinyl Chloride Monomer Manufacturing Operations and Operations Where Polyvinyl Chloride and Copolymere of Polyvinyl Chloride Are Processed, Contract No. CDC-99-74-50, Washington DC, US Department of Health, Education, and Welfare, National Institute for Occupational Safety and Health, pp. 1-8, 101-110
M enechler, D. (1976) Chem ical r e a c tiv ity , b io tra n a fo rm a tlo n ,
- i t y o f p o ly c h lo rin a te d a lip h a t ic com pounds. CRC C r l t . Rev,
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432
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------------------
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--------------
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us E nvironm ental P ro te c tio n Agency (1974b) P re lim in a ry AaBeeament o f the E nvironm ental Problems A ssociated w ith V in y l C h lo rid e and P o ly v in y l C h lo rid e . September, W ashington DC
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IARC MONOGRAPHS VOLUME 19
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" --------
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VINYL CHLORIDE AND POLYMERS
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IARC MONOGRAPHS UOUJTC 19
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IAHC Monographs on the Evaluation of the Carcinogenic Ri8k of Chemicals to Hunane (1979)S Volume 19
VINYLIDENE CHLORIDE and VINYLIDENE CHLORIDE-VINYL CHLORIDE COPOLYMERS
439
Vlnylldene chloride
1. Chemical and Physical Data
1.1 Synonyms and trade names Chea. Abstr. Services Reg. No.: 75-35-4
Chea. Abstr. Name: 1,1-Dlchloroethene
1,1-Dlchloroethylene; aaym-dlchloroethylene
Sconatex
1.2 Structural and molecular formulae and molecular weight
C2H2C12
H Cl
>c=c<
H Cl
Hoi. vt: 97.0
1.3 Chemical and physical properties of the pure substance
Prom Weast (1976), unless otherwise specified (a) Description: Clear liquid with a oweet odour (Hardle, 1964;
Wlndhols, 1976) (b) Boiling-point: 32C (Wlndhols, 1976)
(c) Melting-point: -122.1C
(d) Density: d 1.218; vapour density, 3.4 (air = 1) (Anon., 1972) 20
(e) Refractive Index: n^ 1.4249 (_f) Spectroscopy data: X vapour <200 na; Infra-red, nuclear
magnetic resonance and mass spectral data have been tabulated (Graseelll 4 Ritchey, 1975).