Document KJnzmY0BJjaOpq6MwRzBRR1y6
Air Products and Chemicals, Inc.
Box S3S, Allentown, PA 18105 (215)393-4911
8 Hay 1980
Docket Officer Docket H-034 Room 56212
U.S. Department of Labor, OSHA 200 Constitution Avenue, N.W.
Washington, DC 20210
Sir:
Air Products and Chemicals submits herewith its response to the request for information on vinyl chloride and polyvinyl chloride by The Department on 18 December 1979 (44FR74928 and 4-5FR6668).
This submittal consists of two p^rts:
I. A bibliography of articled on these substances, selected to include those articles published since the 1974 rulemaking procedure on vinyl chloride which are not included in the preliminary bibliography transmitted by R. Appledoff to J. Hadley with a letter of 10 January
1980, and not presented of discussed at the joint conference in 8ethesda on March 20-21, (980. These articles therefore are presumably new information for OSHA.! You are urged to study each document, but for your convenience a br^ef author abstract, if available, or other
summary is included. |
II. Comments on the paper and I discussions of the Bethesda conference
(45FR12560).
'
Please address any questions relating to this submittal to the undersigned.
OTB/rw 699-N-3 Attachment
bcc: R. Fleming / J. E. Hadley - Keller and Heckman
R. H. Schenck H. 0. Smith L. B. Tepper
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Part I
Additional Literature Submitted for the Record and for the Consideration of
the Secretary.
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For the convenience of the reader!, this bibliography is divided into sections by subject. Author abstracts ard provided where available, otherwise short summaries are given. The reviewer is urged to consult the original document for complete details.
A. Analytical Studies
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B. Angiosarcoma Surveys
C. Animal Studies Metabolism
D. Birth Defects, Mutagenicity
E. Chromosomal Effects
F. Dust Studies
G. Environmental Studies
H. Morbidity Studies
I. Mortality Studies
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2Analytical Studies Hoffmann, 0. et al., (1976) Chromatographic Determination of Vinyl Chloride in Tobacco Smoke. Analytical Chemistry 48 47-50 A chemical-analytical meth od has been developed for the quantitative determination of vinyl chi oride (VC) in tobacco smoke. VC from the mainstream smoke is trappe d on charcoal, extracted, and subsequently converted to 1,2-dibromo-l -chloroethane (DB-VC). the latter is enriched by column chromatography cind determined by gas liquid chromatography using an electron capture detector with a high sensitivity for DB-VC. From the mainstream smoke of a popular 85-mm cigarette without filter tip, we isolated 12.2 ng c f VC per cigarette. The VC content in the smoke of some domestic anc foreign cigarettes and little cigars ranged from 5 to 27 ng, and that of a marijuana cigarette was 5.4 ng. The analytical data suggest th at the total inorganic chloride in tobacco is < determining factor for the: amount of VC in the smoke. VC may also be released into our respiral ory environment during the burning of other chlorine-containing organi c matter.
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Angiosarcoma Surveys
Baxter, P. J. and Fox, A. ,1. (1976) Angiosarcoma of the Liver in PVC Fabricators. Lancet, 245.
A review of 707 deaths amofig fabricator workers in 1970-72 found no angiosarcoma and no excess of deaths from cancer at other sites.
Dalderup, L. M., et al. (11976) Angiosarcoma of the Liver. Lancet, 246.
A review of all angiosarcoma deaths in Holland since 1950 found none which had "any traceable contact with vinyl chloride".
Barr, J. T., (1976) Letter to J. T. Smith, EPA, April 6.
Reference to EPA statements that there were no known cases of "neighbor hood" angiosarcoma found by the Agency searches (entire document at tached).
Barnes, A. W. (1976) "Inst itutional Interactions in Problems of Occupa-
tional Health: An Industry View on the Lessons from Vinyl Chloride". Medichem 4th International Conference, HAIFA.
A review of data on angios arcoma cases (entire document attached).
Saric, M. et al., (1976) "Malignant Tumors of the Liver and Lungs in an Area with a PVC Industry". Environmental Health Perspectives, 17 1.89.
The incidence of malignant tumors of the lung and bronchus and of cytologically confirmed primar / malignant tumor of the liver was analyzed for a four-year period in a ci ty with several factories, including a PVC industry. Prior to the st udy two cases of angiosarcoma of the liver were diagnosed in workers emplo yed in PVC production.
The total incidence of ana lyzed tumors was only slightly higher than
predicted. The tumors of t he liver recorded did not show any dependence
on place of work or reside nee. During the period of observation, malignant tumors of the bronchu s (lung) were not recorded in the PVC Industry
Their rate in the area in which the PVC industry is situated was approximately the same as that f or the entire city area.
The study does not indicate that the occurrence of malignant tumors other than angiosarcoma is associated with exposure to vinyl chloride.
Baxter, P. et al., (1977) "Angiosarcoma of the Liver in Great Britain, 1963-1973 Preliminary Study". British Medical Journal, 2, 919.
Deaths attributed to prima ry angiosarcoma of the liver (ASL) in Great
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Britain between 1963-73 we re reviewed by material to a panel of histopathologists
submitting available histological and by obtaining full occupational
and residential histories for the cases agreed as ASL by the panel. On
average four recorded case s of ASL occurred a year, but in only one^third
of the cases submitted did the panel agree with the original diagnosis,
Only one of the agreed cas es could be confidently associated with exposure
to vinyl chloride.
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International Plastics News (1978). Britain's OSHA has Second Thoughts About VCH. Plastics World, 42 (entire article attached). Gehring, P. J., et al., (1979) Risk of Angiosarcoma in Workers Exposed to Vinyl Chloride as Predicted from.Studies in Rats. Toxicology and Applied Pharmacology 49, 15-21. Dose-response data for the induction of angiosarcoma in rats exposed to various levels of vinyl chloride (VC) together with attendant biotransformation data were used th estimate the risk of developing angiosarcoma in persons exposed to VC. [Since a biotransformation product of VC, not VC per se, is responsible for the induction of angiosarcoma, the body surface area of people relative to rats was used to estimate the dose of the carcinogen biotransformed from VC by the former. Four models were used to extrapolate the data. Using a probit model, 10 hepatic angiosarcomas were predicted to occur in:a recently reported epidemiological cohort of 9677 workers whereas five have occurred. Linear models and that based on the equation, Risk = 1 - ej , where x = dose, do not appear as reliable. For an eight-hour day, fivh days/week, 35-year time-weighted, average exposure of 1 ppm, the predicted incidence of hepatic angiosarcoma using the probit model is 1.5 x 10 .
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C. Animal Studies * Metabolisih
lf|ppus, et al., (1975) Rat Liver Microsomes Catalyse Covalent Binding of C-Vinyl Chloride to Macromolecules. Nature 257 134.
The authors find covalent binding of VC metabolites provides additional support for an active intermediate as the actual carcinogen.
Bolt, et al., (1975) Metabolism of Vinyl Chloride. Lancet 1425.
Results similar to Kappus, et al.
Green, T. and Hathway, D, [1975) The Biological Fate in Rats of Vinyl Chloride in Relation to i ts Oncogenicty. Chem-Biol. Interactions. ]]_ 545.
The main eliminative route for ^C] vinyl chloride after oral, i.v. or i.p. administration to rat is pulmonary; both unchanged vinyl chloride and vinyl chloride-related C0? are excreted by that route and the other [ 4C] metabolites via the kidneys. After intragastric administration, pulmonary output of unchanged vinyl chloride is proportional to the logarithm of reciprocal dose. Excretion patterns after i.v. and i.p. injections are predictable from the characteristics of excretion following oral administration. Pulmonary excretion of unchanged vinyl chloride after oral dosing is complete within 3-4 h, but pulmonary elimination of CO, and renal excretion ofimetabolites occupies 3 days. In comparison, 99* of a small i.v. dose ii excreted unchanged within 1 h of injection; 80% within 2 min.
The rate of elimination of single oral doses of C^C] vinyl chloride is uninfluenced by up to 60 tys' chronic dosing with the unlabeled substance.
The distribution volume ofjvinyl chloride as displayed by whole-animal autoradiography agrees with deductions from excretion data. Small local ization of u in the para-auricular region of appropriate sections occurs in sectioned tubules, belonging possibly to the Zymbal glands.
Biotransformation of vinyl chloride into S-(2-chloroethyl) cysteine and N-acetyl-S-(2-chloroethyl) cysteine occurs through addition of cysteine, and biotransformation into: (i) chloroacetic acid, thiodiglycollic acid and glutamic acid, and (ill into formaldehyde (methionine, serine), C0 and urea is explicable in perms of an associative reaction with molecular
involving a singlet oxyden bonded transition state in dynamic equili brium with a cyclic peroxiie ground state. There is no evidence for chioroethylene oxide formaiion.
Thiodiglycollic acid is th^ major metabolite of chloroacetic acid in rats; more than 60% of the dose.
The interaction of vinyl chloride and of its primary metabolites with the intermediates of mammalian metabolism is discussed in relation to the oncogenicity of that substinee.
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Reynolds, E. S. , et al., (1975) Hepatatoxicity of Vinyl Chloride and 1,1-dichloroethylene: Rolfe of Mixed Function Oxidases. Presented at the 59th Annual Meeting of the Federation of American Societies for Experimental Biology, Atlantic City, New Jersey, April 15.
Vinyl chloride, an occupational carcinogen, produces acute liver injury
in rats pretreated with phenobarbital or Aroclor 1254. Injury appears related to morphologic changes in the endoplasmic reticulum. Degree of injury as indicated by elej/ation of serum enzymes derived from the liver correlates with magnitude tf induction of cytochrome P-450 and its reduction by NADPH. Hepatic injury following 1,1-dichloroethylene differs strikingly
and appears to involve plajsma membranes, mitochondria and chromatin,
sparing endoplasmic reticullum. In contrast to vinyl chloride, induction of cytochrome P-450 appear^ to protect against 1,1-dichloroethylene.
Withey, J. R. (1976) Pharmbcodynamics and Uptake of Vinyl Chloride Monomer Administered by Various Routes to Rats, 0. of Toxicoloqy and Environ.
Health, 1 381.
To assess the hazard presented by the oral ingestion of vinyl chloride
monomer, rats that had been surgically prepared with an indwelling jugular cannula were dosed by intr.igastric intubation with aqueous solutions
containing up to 2.0 mg/ml vinyl chloride. Time-concentration curves were obtained from sequent! al samples of blood. The uptake of vinyl
chloride by this route was found to be extremely rapid; peak concentrations were achieved lest than 10 min after administration of the dose, Elimination from the blood compartment appeared to be biexponential.
Studies with the same animal model in a single restraint cage that allowed a "head only" exposure to concentration of vinyl chloride up to 7,000
ppm in the gas phase have shown a similar rapid uptake followed by a plateau blood concentration during several hours of exposure. On removal from the vinyl chloride atmosphere, blood levels.fell rapidly to barely detectable concentrations ifter 2 hr.
The precise kinetic coefficients that describe the distribution and elimination rates of vinylichloride from the blood compartment were also
determined from the blood Concentration data after the administration of
an intravenous dose of aquious or vegetable oil solution.
Guengerfch, F. P. and Strickland, T. W. (1977) Metabolism of Vinyl Chloride Destruction of the Heme of Highly Purified Liver Microsomal Cytochrome P-450 by a Metabolite. Molecular Pharmacology, 13 993.
The NADPH-dependent, vinyljchloride-mediated destruction of cytochrome
P-450 was demonstrated in rat liver microsomes and in highly purified
reconstituted enzyme systems containing NADPH-cytochrome P-450 reductase
(NADPH:ferricytochrome oxidoreductase, EC 1.6.2.4) and cytochrome P-450.
This loss of cytochrome P-450 but not to lipid peroxidatjon
could be attributed to heme or binding of electrophiles
destruction, to free sulf-
hydryl groups. The system required all components necessary for mixed-
function oxidation, including molecular oxygen, and was inhibited by
carbon monoxide, suggesting strongly that oxidative metabolism of vinyl
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chloride by cytochrome P-4 50 is necessary for the observed destruction.
The NADPH-cytochrome P-450 reductase-catalyzed destruction of free and cytochrome P-450-bound heme was also observed In reconstituted systems in the absence of vinyl chloride. Inhibition experiments with carbon monoxide
and catalase suggest that the vinyl chloride-mediated destruction of cytochrome P-450 heme differs from these processes. Two proposed metabolites
of vinyl chloride, vinyl clhloride epoxide and 2-chloroacetaldehyde, do not appear to be responsible for the heme destruction. Evidence for the Involvement of free radicals could not be demonstrated when the reaction was examined by EPR spectrloscopy or when attempts were made to inhibit cytochrome P-450 destruction v/ith radical-trapping agents.
Hathway, D. (1977) Comparative Mammalian Metabolism of Vinyl Chloride and Vinylidene Chloride ih Relation to Oncogenic Potential. Environ.
"H"ealth Perspectives. 21 5$j .
Elucidation of the role of vinyl chloride metabolites In the various reaction sequences which Comprise the metabolic pathway, including the interaction of reactive metabolites with some purine and pyrimidine residues of target-organ DNA, provides some explanation for the (oncogenic) properties associated with the original substance. Comparative investi
gation of the biological fate of vinylidene chloride reveals an agent of low oncogenic potential w^ich Is likely to be damaging only under special
curcumstances, and speciei differences which suggest that the mouse is more susceptible than the[rat towards vinylidene chloride oncogenicity.
Green, T. and Hathway, 0. (1977) The Chemistry and Biogenesis of the S.
Containing Metabolites of. Vinyl Chloride In Rats. Chem. Biol. Interact.
17 137.
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In order to determine whether vinyl chloride yields chloroethylene oxide in vivo, the biogenesis ojf the various urinary S-contatning metabolites in rats has been investigated.
N-Acetyl-S-(2-hydroxyethyl) cysteine is a major vinyl chloride metabolite in rats, but according to1 the method of protective esterif`cation that is used, so either N-acetyl-S-(2-chioroethyl) cysteine or N-acetyl-S(2-hydroxyethyl)-cysteine may be isolated from the body fluids.
N-Acetyl-S-vinylcysteine is a second related metabolite. These Scontaining vinyl chloride metabolites are not mutagenic in S. typhi-
murium. Neutral methanol methylates N-acety1-$-(2-hydroxyethyl)cysteine. N-Acetyl-S-(2-methoxyethyl)cysteine plus N-acetyl-S-vinylcystelne degrade to give the volatile S-(^-methoxyethyl)(prop-1 or 2-enyl)sulphide.
Administration of several vinyl chloride metabolites and closely related
compounds to rats shows that chloroacetaldehyde and S-(carboxymethyl)-
cysteine, but not chloroacetic acid, lie on a pathway or pathways
connecting vinyl chioride) with thiodiglycollic acid. The fact (a) that
chloroacetaldehyde affords both thiodiglycollic acid and N-acetyl-S-
'(2-hydroxyethyl)cysteine in the animal and (b) that S-(carboxymethyl)
cysteine has been identified amongst the hydrolytic products from an
hepatic extract prepared from vinyl chloride-treated animals Is consistent
with the formation of chloroacetaldehyde, and with the reaction of chloro
ethylene oxide or chloroacetaldehyde with glutathione in the presence of a
glutathione S-epoxide transferase to give the identified S-containing
metabolites.
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Buchter, Bolt, et al., (1978) Pharmacokinectics and Carcinogenesis of VC. Verh Oeutsch Ges. Arbeitsmed. 18 111.
A discussion of the relati metabolism, enzyme saturation, and clearance mechanisms of vinyl chlori de in humans and rodents.
Vainio, H. (1978) Vinyl Chfl oride and Styrene - Metabolism, Mutagenicity and Carcinogenicity. Chem Biol. Interacts. 22 17.
Vinyl chloride and vinyl bfenzene (styrene) are mutagenic in microbial
tests, in Drosophila, in yeast, and in mammalian cells. Reports from various countries have shown an excess of chromosomal aberrations in the
lymphocytes of workers exposed to vinyl chloride monomer when the workers were compared with control*. Workers occupationally exposed to styrene also revealed a clear increase in the rate of chromosome aberrations in their lymphocytes. Both ciloroethylene oxide and styrene oxide, the primary biotransformation Products of vinyl chloride and styrene respec tively, bind covalently to cellular macromolecules. Vinyl chloride is a carcinogen in both animals and man. Styrene is currently being tested in animals. These findings, the demonstration of mutagenic response via microbial and other test systems and with observations of significant
excesses of chromosomal aberrations among workers exposed to these agents, raise scientific and health-oriented concern about the possible genetic
risks of vinyl chloride an|i styrene to man.
Green, T. and Hathway, D. (1978) Interactions of Vinyl Chloride with Rat Liver DNA in vivo. Chem. Biol. Interact. 22 (2-3) 211.
Vinyl chloride-derived chloroethylene oxide and/or chloroacetaldehyde
behaves as a bifunctional alkylating agent towards deoxyadenosine and
deoxycytidine residues of j)NA. The separation of DNAs and the 2 etheno-
deoxyribosylnucleosides bylliq. chromatog., and the mass spectra of
ethenodeoxyadenosine and ethenodeoxycytidine and of their O-bis(trimethylsilyl)
derivs. are described. In the animal expt. (ii), the resulting proportion
of ethenodeoxyadenosine wa small compared with that of ethenodeoxycytidine.
Ethenoadenine (imidazo [2,l-i]purine was identified: (a) in the supernatant
after sedimentation of the modified DNA in the model expt. (i), and (b)
in the product resulting from the reaction between chloroacetaldehyde and
deoxyadenosine. The effect on the structure of DNA of the imidazo cycli-
zation of deoxyadenosine ajid deoxycytidine residues and of the depurination
of ethenodeoxyadenosine residues is discussed in relation to vinyl chloride
oncogenicity.
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Winell, M. , Holmberg, B. , (jCronevi, T. (1977) A possible correlation
between biochemical changes and pathological findings in VCM - exposed mice and hamsters. Int. Symp. Control Air Pollut. Part 1., p, 152.
Mice and hamsters were exposed by inhalation to 50 and/or 500 ppm vinyl chloride during 6-18 mo. Blood samples were taken at regular intervals
`during the exposure for anal, of plasma enzymes indicative of liver damage or early malignancy Some animals were sacrificed for histopathol. examns. after 6 mo. and the rest were examd. when dead or moribund. Aik.
phosphatase and total lactate dehydrogenase (LDH) activities were elevated
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in VCM exposed mice. There was also a shift towards cathodic isoenzymes of LDH. The transaminases were not significantly elevated. No changes in plasma enzymes were found in exposed hamsters. Pathol, examn. of VCM-exposed mice showed the presence of hemangiosarcomas in fat tissue, histol. benign alveologeni|c lung adenomas as well as a few benign and malignant tumors at various sites. Only one liver hemangiosarcoma was noted.
No liver fibrosis was seed, All mice exposed to 50 ppm VCM for 76 mo. developed tumors. Tumor ncidence was high also in the hamsters. Enzyme changes occurred late in the study, subsequent to tumor appearance. The value of enzyme changes as a diagnostic criterion on tissue injury or early malignancy caused by VCM was discussed.
Stockle, G., Laib, Filser, Bolt (1979) Vinylidene Fluoride: Metabolism and Induction of Preneopla Stic Hepatic Foci in Relation to Vinyl Chloride. Tox Letters 3 337.
The velocity (Vmax) of metabolic elimination of vinylidene fluoride from the rat is 1/100 that of \^inyl chloride. In the light of the current concept of metabolic activation of halogenated ethylenes, this may explain the much lesser ability of vinylidene fluoride, compared with vinyl chloride, to induce pre-neoplastic "ATPase,,-deficient hepatic foci in newborn rats.
Laib, Stocklc, Bolt, Kunz (1979) Vinyl Chloride and Trichloroethylene, Comparison of Alkylating Effects of Metabolites. J. Cancer Res. Clin. Oncol. 94 139.
[1,2-^C] Vinyl chloride a nd [1,2- 14C] trichloroethylene were incubated with rat liver microsomes, NADPH and RNA (from yeast). Whereas trichloroethylene metabolites were irreversibly bound to proteins in microsomal incubations to a higher ex^.ent than vinyl chloride metabolites, irrevers ible binding to RNA was lower for trichloroethylene metabolites. ,Hydrolysis of the RNA which was reisolated from microsomal incubations with ^C-vinyl chloride or u-trichloroethylene and separation of the nucleosides, showed different alkylation products arising from vinyl chloride and from trichloroethylene, characteristic for vinyl chloride being formation of 1,N -ethenoadenosine and 3,N -ethenocytidine. The different reactivities of metabolites of vinyl chloride and of trichloroethylene prompted a comparison of the oncogenic effects of both compounds against the rat liver cell. Newborn rats were exposed for 10 weeks to 2000 ppm vinyl chloride or trichloroethylene (8 h/day; 5 days/week). After this period livers of the animals were stained for nucleoside-5-triphosphatase. Whereas the vinyl chloride-exposed rats showed focal hepatocellular deficiencies in this enzyme, which are supposed to represent an early sign of malignancy, no such changes were induced by trichloroethylene exposure. The data therefore suggest differences between the hepatocarcinogenic activity of vlinyl chloride and possible effects of trichloro'ethylene on the liver.
Zajdela, F. et al,, (1980) Carcinogenicity of Chloroethylene Oxide. Cancer Research 40 352.
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Repeated s.c. administration of chloroethylene oxide, a reactive metabolite
of the carcinogen vinyl chloride, induced local tumors in mice, with an
incidence comparable to trtat of bis(chloromethyl)ether, a structurally
related human and animal carcinogen, when both compounds were applied at
maximum tolerated chronically toxic doses; no tumors distant from the
injection site were produced. Bis(chloromethyl)ether, chloroethylene
oxide, and its rearrangement product chloroacetaldehyde, a highly toxic
compound, were further tested in an initiation-promotion experiment.
Application to the skin a single dose of either bis(chloromethyl)ether
of chloroethylene oxide, followed by 3-times-weekly applications of
12-0-n-tetradecanoylphorbcil-13-acetate for 42 weeks, produced skin tumors
in mice; chloroacetaldehyde under comparable conditions produced no
increase in benign or malignant tumors. A good correlation between the
chemical reactivity, on tfje basis of hydrolysis constants in aqueous
media, and the carcinogenicity of the three compounds was noted. Our
results support the hypothesis that epoxidation of the ethylenic double
bond in vinyl chloride yields an ultimate carcinogenic metabolite, chloro
ethylene oxide, a highly reactive compound which appears also to be
largely responsible for the known genetic changes caused by the parent
compound.
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D. Birth Defects. Mutagenicity
Speros, J.: (1974) Telegraph Survey Indicates No Link to PVC. Defects Painsville, OH, Telegraph, Sept. 11.
Entire article attached.
Center for Disease Control: (1975) Vinyl Chloride and Congenital Malformations-Ohio. Morbidity and Mortality Weekly Report 24 245.
A follow-up story on reported CNS malformations in Ohio "could not establish any association between cases and vinyl chloride exposure".
Edmonds, L. D., Falk, H. a id Nissim, J.: (1975) Congenital Malformations and Vinyl Chloride. Lancet, 1098.
"No association was found with vinyl chloride exposure".
Purchase, I. F., Richardsoh, C. R., Anderson, D.: (1975) Chromosomal
and Dominant Lethal Effect^j of Vinyl Chloride. Lancet, 410.
Because of reported elevated chromosomal breaks in exposed humans, a dominant lethal test was carried out on mice, which was negative. The authors conclude that VC does not affect the stem cells.
Paddle, G. M.: (1976) Genstic Risks of Vinyl Chloride. Lancet. May 15.
A criticism of the Infante paper on fetal wastage in wives of exposed workers.
Edmonds, L: (1976) Birth befects and Vinyl Chloride: Prac. Conf. on Women and the Workplace, Washington, D.C., p. 114.
A review of the above papers on the Ohio and West Virginia studies. No connection was found with vinyl chloride and birth defects.
Edmonds, et al., (1976) Congenital Central Nervous System Malformations, Kanawha County, W. Va., Public Health Service EPI-76-60-2, Atlanta, duly 26.
Data available through the Birth Defects Monitoring Program (BDMP) revealed that from 1970 through 1974, Kanawha County, West Virginia--where 1 of the 40 polyvinyl chloride production plants in the United States is located--had rates of congenital central nervous system defects that were significantly higher than Rational BDMP rates for those years.
In February 1976 an investigation was undertaken because of the possibility that these higher than expected rates may have been related to parents' occupational or residential exposure to vinyl chloride. The study confirmed that an increase in CNS defect rates had occurred in Kanawha County, and cases clustered primarily in the area east of the plant; however, no re lationship between infants with malformations and parents1 exposure to vinyl chloride could be established.
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Downs, Stallones, Frankowski, Laberthe: (1977) Vinyl Chloride. Birth Defects and Fetal Wastage - A Critical Review. Prepared for the Society of the Plastic Industries, Inc. Unpublished.
We have reviewed the avail ible pertinent literature on vinyl chloride and birth defects and fetal wa?tage. Individual studies in a particular area have been assessed for the strength and validity of their conclusions,
and the several studies in each area synthesized, accordingly, by taking
into account the consistenty, strength, specificity, temporal patterns and coherence of the study results.
In summary, we have concluded that, to date, (A) there is some evidence of an association between j/inyl chloride and chromosome aberrations in lymphocyte cells of vinyl thloride workers, (B) there is no evidence of
an association between vinyl chloride and excess fetal wastage in wives
of VC workers, and (C) there is no evidence of an association between vinyl chloride and excess birth defects in communities with PVC production
facilities.
The task of collating the existing literature on vinyl chloride and birth defects, and arriving at general conclusions therefrom, has not been an easy one. The difficulties have been enhanced by the poor quality of
many of the study designs,! and by inappropriate and misleading statistical methods. The methods of selecting control groups for the epidemiologic
studies has been, to say tlhe least, very disturbing. We fervently hope greater efforts will be devoted in future studies to improvement of study
methodologies and designs.
Henschler, D. and G. Bonse (1977) Metabolic Activation of Chlorinated Ethylenes: Dependence of Mutagenic Effect on Electrophilic Reactivity of the Metabolically Formed Ejpoxides. Arch. Toxicology. 39 7-12.
In chlorinated ethylenes, jthe chlorine substitution exerts, by its electron
withdrawal effect, a stabilization of the molecule which increases with
the number of chlorine residues. All chlorinated ethylenes are metabolical ly
transformed, in a first stlep reaction, to epoxides which may rearrange to
aldehydes or acyl chlorides, respectively, undergo hydrolysis to diols,
conjugate with glutathione, or react, by alkylation, with cellular macro
molecules. The electrophilicity of the epoxides is high with those
having an unsymmetric chlorine substitution, and comparatively low with
the others bearing symmetric chlorine residues. According to in vitro
mutagenicity testing in a modified Ames system, the following rule on
structure/activity-relationship has been worked out: mutagenic potential
is bound to unsymmetric substitution and high chemical reactivity (as
with vinyl chloride, vinyjidene chloride, and trichloroethylene), symmetric
substitution results in Hwer chemical reactivity and non-mutagenicity.
So far* the rule is substantiated by positive carcinogenic effects in
animal experiments with vfnyl chloride, vinylidene chloride and trichloro-
, ethylene.
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Hopkins, J. (1979) Vinyl thloride - Part 2: Mutagenicity, Fd Cosmet. Toxicol., 17 (5) 542.
A review.
AP00048786
-13Peter, $. , and G. Ungwaryi Lack of Mutagenic Effect of Vinyl Chloride Monomer in the Mammalian Spot Test. Mut. Res. , 77 193 (1980). The authors conclude that although vinyl chloride has been shown to cause point mutation in bacteria, their tests with color-coat mosaic reversions in mice at 4,66>0 ppm "provides no evidence that VCM induces somatic gene mutation."
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E. Chromosomal Effects
Picciano, 0. J., Flake, R. E., Gay, P. C., Kilian, D. J. , Vinyl Chloride
(1977) Cytogenetics. Journ|al of Occupational Medicine, 19 527-530.
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This report presents cytodenetic findings from a group of 209 workers employed for up to 28 years in the manufacture of vinyl chloride monomer
at the Texas Division of Dow Chemical U.S.A. Cytogenetic evaluation results from this group were compared to results found in examination of Individuals being considered for employment. Statistical analyses were
performed on a group basis for chromatid aberrations, chromosome aberrations
and proportion of abnormal cells; no statistical difference of significance
was found between the two groups. Comparison of these results with reported
studies suggests that the level of cytogenetic aberrations in vinyl chloride workers is probably related to the length and level of exposure, and that risk of adverse denetic effect can be avoided in controlled, minimal-exposure environments.
MacMahon, B., Vinyl Chlori de and Reproduction. A literature review, prepared for the Society o f the Plastics Industry, Inc. , and submitted to the Environmental Protecti on Agency in response to the Proposed Amendment
to the National Emission S tandard for Vinyl Chloride, August 11, 1977.
In short, until more and better studies are available, vinyl chloride monomer must be regarded as potentially mutagenic to man, and at leaast in high doses potentially teratogenic. However, except for the evidence of chromosome breakage in heavily exposed workers - evidence which itself cannot be regarded as defi nitive * the literature to date contains no
credible evidence that vinyl chloride has actually caused mutations. fetal abnormal-ties, or fet al death in humans.
Fleig, I., Thiess, A. M. (jl978) Seminar in Occupational Medicine. Mutagenicity of Vinyl Chloride J. Occu^. Med., 20 557-562.
A review. Published data show no conformity of results.
Hansteen, I-L, et al., (1978) Effects of VC in Man: A Cytogenetic follow up study. Mutation Research 78 271.
Cytogenetic studies were performed on 39 workers from a PVC plant in 1974. Sixteen healthy men without any connection with the plant were
chosen as controls. The c|ytogenetic study was repeated for 37 of the 39 workers 2-2 1/2 years late r. During this time interval the workers had
only had a minimal exposur e to VCM. This repeated study was performed with 32 matched controls rom the office employees in the factory.
Breaks, gaps and stable rearrangements were scored in 100 metaphases per person from 48 hour lymphocyte cultures.
The mean chromosome breakage frequency for the workers (3.41 per cent) was significantly higher than for the controls (1.79 per cent) in the first investigation. In the repeated study no difference was found in mean chromosome breakage frequency between the workers and their matched
AP00048788
-15controls. Neither was there any difference between these breakage frequencies and the breakage frequency for the previous control group. These results might indicate a relations hip between the reduction in exposure to VCM and the normalized chromos ome breakage frequency. Sister chromatid exchanges were studied fori 16 workers with matched controls in the repeated study. A mean of 7.6 SCE' s per call were found for both workers -and controls.
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F. Dust Studies
Waxweiller, R., Smith, A., Tyroler, H., Falk, H.: (1978) An Epidemiologic Investigation of an Excess Lung Cancer Risk in a Synthetic Chemicals Plant. 19th Inter. Conf. o n Health. Dubrovnic. Yugo.
The authors find that lung cancer rates are not related to VC exposure, and hypothesize that dust nay be a factor, although several possible confounding agents, includ ing smoking, were not controlled. They con clude that more studies are needed to confirm the eitological agent.
NIOSH (1977) Exposure of R^ts, Guinea Pigs and Monkey to PVC dust. May, unpublished.
Rats, guinea pigs, and monkeys were exposed to 10 rng/m^ respirable PVC dust for 6 hrs/day, 5 daysK/eek for 22 months for monkeys and 12 months for rats and guinea pigs. I No lung or liver damage was found, either acute or chronic, nor was kny carcinogenicity observed.
Johnson, W. and R. E. Schmidt, Effects of PVC Ingestion by Dogs. Am. J. Vet. Res. 38 1891 (1977) j
With the exception of occasional soft feces, abnormal clinical signs were not seen. The test material was observed to pass through the digestive system of all animals unchanged. Results of hematologic examination, blood chemical analyses, akd urinalyses were within normal values in all dogs throughout the testing periods. Gross and microscopic lesions attributable to the test material were not seen.
Wakeman, I. and Johnson, H 0978) Vinyl Chloride Formation from the Thermal Degradation of PVC Polymer Eng. Science, 18 404.
The volatile products from the thermal degradation of poly(vinyl chloride) (PVC) resins and compounds are shown to contain'trace amounts of vinyl chloride. Data presented show the effect of temperature and resin type on the amount of vinyl chloride formed. At the maximum temperatures involved in PVC processing which may reach 210C, vinyl chloride monomer (VCM) evolution amounts to less than 1 ppm (resin basis). A technique employing a thermogravimetric balance and charcoal adsorption of volatiles is described for studying thermal degradation of PVC. The volatiles are analyzed for vinyl chloridu by gas chromatography. Peak identity was confirmed by mass spectrometry.
Richards, R. J. et al., (1975) Biological reactivity of PVC dust. Nature 256 664.
From these preliminary findings we conclude that certain forms of PVC dust exhibits a high haemolytic potential because of the presence of a readily soluble, surface associated agent.
Costa, V., and Frongia, N. '(1978) Historical and Ultrastructural obser vations on the peritoneal changes induced by the endoabdominal inoculation of a sinqle dose of polyvinyl chloride powder (PVC) in rats, Sard Medical Review, 81, 217-226.
AP00048790
-17The inoculation Into the abdominal cavity of rats of a single dose of PVC powder caused a granulomatous non-inflamatory reaction of the peritoneum that histologically and ultrastructurally appears fairly typical, and perhaps exclusive, for this substance. Furthermore, it is pointed out that after seven months from the inocluation no changes even ultrastrucjtural indicative of a possible neoplastic evolution were observed in the examined rats.
4
AP00048791
18G. Environmental Studies
Hill, J., (1976) Oynamic Behavior of Vinyl Chloride in Aquatic Ecosystems. Environmental Research Laboratory, Athens, GA, January, PB-249-302. VC is not absorbed or converted by several common components of ecosystems, nor is there evidence for ^accumulation. Escape from these systems is rapid because of the high /apor pressure.
i
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-19-
H. Morbidity Studies
|
Maricq, H. R. et al., (19/6) Capillary Abnormalities in Polyvinyl Chloride Production Workers. JAMA 236 1368.
Examination by wide-field capillary microscopy of the hands of 152 workers in vinyl chloride (VC) po ymerization plants demonstrated scattered,
scleroderma-like microvasc ular abnormalities in 21 workers and isolated capillary abnormalities 1 27, as compared with only three isolated abnormalities in 50 manual Workers not exposed to vinyl chloride. Thirteen of 17 VC workers with obj ictive evidence of VC-associated abnormalities (angiosarcoma or fibrosis of liver, acroosteolysis, or scleroderma-like skin lesions) were observed to have microvascular abnormalities.
If prospective studies confirm the implications of this study, capillary
microscopy may become a uieful mass-screening procedure in the early de tection and prevention of I VC-associated disease.
Gamble, J. et al., (1976)jEffect of Occupational and Nonoccupational Factors on the Respirator! System of Vinyl Chloride and other Workers, Journal of Occupational Medicine, 18 659.
There are suggestions in he literature that vinyl chloride (VC) acts as a lung irritant. Respira ory questionnaires and lung function tests were administered to 174 chemi al (VC) workers, 81 polyvinyl chloride (PVC) workers, 72 former VC wor ers, and 136 ruuber workers, and 68 maintenance workers with exposure to C, PVC, and rubber. Except for small airways
Iobstruction associated wi h rubber, increased respiratory symptoms and
decreased pulmonary funct on were not associated with working in chemicals, plastics, or rubber. Son increases in baseline pulmonary function were associated with VC exposu e. Acute reductions in pulmonary function were observed in smokers orking in chemicals, plastics, and rubber, Heavier cigarette smokers over 40 years of age had the most adversely affected respiratory system.
Work was not associated with chronic respiratory effects, but all exposure groups experienced some aiute respiratory insult.
t
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-20-
Mortality Studies
|
Duck, B. Carter, J., (1975) Coombes, E.: Mortality Study of Workers in a Polyvinyl Chloride Production Plant. Lancet, 1197.
Age-standardized mortality rates for a population of 2100 male workers
exposed to vinyl chloridejfor periods of up to 27 years do not show any
excess of total or cause-ipecific mortality. One case of angiosarcoma of
the liver was identified just outside the study period. There was no
suggestion of an increased frequency of deaths from the more common
malignant diseases.
\
Wagoner, J., Infante, P. dnd Saracci, R. Vinyl Chloride and Mortality Lancet. 194 (1975).
Berry, G., Rossiter, C,, e^lso Fox, A. (1976) Vinyl Chloride and Mortality Lancet. 416, 417.
Polemics on the Duck articjle. Berry and Fox conclude that no effect from exposure is found.
Frentzel-Beyme, R., Schmitz', T., Thiess, A. M.: (1978) Mortality Studies of VC/PVC worker of BASF fjlant. Arb. Socialroed. Practicat., 131.
The results of the prospedtive mortality study of 1,618 VC-PVC exposed persons will be given conclusionally as a supplement to an earlier report in this journal. Proceedings and analysis were based on the usual inter national methods, which m^kes a comparison with other studies possible.
As it was not possible to offer reliable details with regard to the degree of exposure, the mortality of the VC-cohort was investigated by considering VC-exposure periods of 5, 10, 15 years and more than 15 years, with a minimum observation period of 5, 10, 15 years accordingly. The total VC-cohort was further subdivided into groups comprising those who had been exposed beford I960 and those who had their first exposure between 1960 and the dead!line of the study.
Reference mortality figures from:
-- Ludwigshafen (180,000 iphabitants)
-- Rhinehessia-Palatinate (3,6 million inhabitants)
-- Styrene-cohort consisting of 1,960 workers, as an internal control group were taken as a comparison to the VC group.
I The follow-up of all Germah employees was 95.5% successful. However, in the case of the foreign wofkers, all exposed after 1960, the follow-up , was only 60% successful.
The study revealed the following results:
AP00048794
21-
-- angiosarcoma deaths cou Id not be registered -- cirrhosis of the liver ^nd myocardial infarctions were less than expected -- the expected number of hatural causes of death (ICD 0-795) was higher'than
the number of 61 observbd cases -- the unnatural causes of death (ICD 800-999) were nearly as frequently ob
served as expected The following diseases were more frequently observed than expected: -- tuberculosis of the lung -- malignant tumors of the colon and the stomach -- hypertrophy of the prostate They significantly exceeded the expectancy rate although these events only occurred in a few cases. The division of the cohort in groups with exposure beginning before or after 1960, showed after a minimum observation period of 5 or 10 years resp., a higher observed thian expected mortality rate for natural deaths if exposure started before 1960. The duration of exposure h'ad no recognizable influence on an increased rate of mortality after long exposure periods. Observations of other studies were not confirmed that lung cancer, brain tumors and tumors of the liver were observed more frequently after VC exposure, or that VC may be a specific risk to these tumors. The deviations from other published risk-predilections could perhaps be due to a doseresponse effect, as the VCj exposure level within the BASF has always been comparatively low. Peto, R. Distorting the epidemiology of cancer: The need for a more balanced overview. Nature 284 297 (1980). The author presented criti cism of the recent Epstein book "The Politics of Cancer**, and of the NIE HS/NI0SH "Estimates" paper which stated that upwards of 20% of cancer w as occupationally-related. Of the letter document he says "it shows how a group of reasonable men can collectively generate an unreasonable report." A plea is presented for less misrepresentation in the regulatory arena.
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-22-
PART 11 Comments Ion the Bethesda Symposium
f^arch 20-21 , 1980 I. Introduction
Both the procedures used at the Symposium and the papers presented were extremely disappointing because of the lack of a scientific approach in the organization and execution of the symposium. The interval between the call for papers and ttje symposium was too short to permit the preparation of any new orioriginal work, so that what was presented consisted primarily of repjetition of published data. The schedule was so crowded that there was inadequate time for a reasonable exchange of questions and answers between the speakers and the attendees, and in the case of the late afternoon session of the first day, an opportunity to discuss the papers was not provided until the next morning, when it was most ineffective. This crowded schedule also required that several proffered papers be refused. Several of the speakers strained very hard to reinterpret the old datja, to the extent of near misinterpretation in some cases. The situation is exacerbated by the fact that the results will be published in a nori-peer-reviewed journal, thus helping to perpetuate these errors of interpretation. The end result is that th^ Symposium fell far short of a sound or balanced scientific colloquium, and little useful or new information was presented. However, as stated above, many incorrect interpretations of fact were allowed to stand uncorrected. These comments will review a number of such cases, and discuss several other points of interest which were presented.
AP00048796
II. Animal Studies - Vinyl Chloride
A. Professor Maltoni, in the first paper, reviewed the data from his feeding and inhalation studies which he had presented last November in Paris. His data showed a clear no-effect level at 10 ppm and lower exposaves in this lifetime feeding and inhalation and gavage experiments (see page^ 35-38 of the transcript, and again at page 43). i
B. In paper 2, Suzuki reported that vinyl chloride induced a nonmalignant, non-metastAsizing alveolar cell tumor in mice.
C. Paper 3, by Groth, reported that the incidence of angiosarcoma increased and the latency decreased with age in mice when exposed to 948 ppm of vinyl chloride for about 24 weeks at various starting ages. It would appear from these results that the repair mechanism is not as effective in older animals as it is in the younger. (However, these results are contrary to those reported by Stutman (J. Nat. Cancer Inst. 62, 353 (1979), who found a decreased incidence and increased latency period when mice were injected with 3-methylcholanthrene at ages from 30 to 360 days.) There were no significant blood chemistry signals observed in the test animals. There were no angiosarcomas in the tpvo youngest age groups, and lung cancer was not reported.
D. Radike showed, in papAr 4, that ethanol alone is a powerful carcinogen in rats, and that it Creatly enhances the potency of vinyl chloride when animals are exposed to both substances simultaneously. Again, there were no significant findings in blood chemistry differences between exposed and control groups.
E. Paper 5 by Hehir showed that rats and mice exposed to up to 50,000 ppm of vinyl chloride gave no neoplastic response. Mice showed a dose-dependent response in benign adenomas, but no significant progression to carcinoma. He supported Maltoni's conclusion of a no-effect level. He Also reported no deleterious effects on repro ductive performance or( on subsequent generations from the exposures of his study.
i
AP00048797
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-25-
IV. Human Studies - Vinyl Chi ;>ride
A. Maltoni described in paper 8 the results of sputum cytology studies in 6,780 workers from monomer and polymer plants in Italy. He found. a higher dysplasia in the "plastics industry" than some others, that was va_ri_a_b_l_e__a_c_c_o_r_d_in_ ____ to the geographical location of the plant, and which was not affected by the smoking history of the worker. He concluded that "much (remains to be done to qualify the part played by the monomer and thfe polymer in determining the lesion of respiratory tract material among VC/PVC workers."
B. Infante presented a list of 9 human epidemiology studies in paper 9. He concluded that, although none of these gave statistically significant results associated with vinyl chloride for anything other than angiosarcoma, the preponderance of the evidence for so many studies must be considered conclusive. A critical factor which the speaker failed to mention but which was partially acknowledged by Beaumont (tr. p. 174), Is that all of the six United States studies of workers are the same general Cohort. The Tabershaw and Cooper 1974 study is an earlier version of the more complete Equitable Environmental Health study of 1978, which was presented separately as paper 11. The Waxweiler, Manson. Buffler and Ott studies all were of subsets of the EEH cohort, some of which duplicated each other to some degree, and several of which were carefully selected to include those few plants where there were angiosarcoma cases, omitting all the other plants.
Further, the 1975 Duclf study is a major subset of the 1977 Fox and Collier cohort. Thus- there are but three studies which are com parable as separate cchorts, the EEH study of the entire United States, the Byren stucy of two plants in Sweden, and the Fox and Collier study of Great Britain. None of these three comprehensive national studies gave a significant elevation of cancer at sites other than the liver. It is not scientifically sound to attempt to draw separate conclusions from subsets of cohorts, particularly when they were so carefully selected. The Waxweiller study itself points out that if one of its plants were not considered, there would be no elevated incidences. Further, considerable liberties were taken with the data in the Tabershaw, Cooper and Ott subsets in mathe matically manipulating the brain case data to obtain an "estimated" excess incidence. Thq speaker also overlooked the fact that the supposed excesses of dancer at other sites consisted of many different types of cancers, which violates the rule of specificity which is widely accepted. Another failing in the support for the conclusion was the absence of any dose response effect for the other sites. Therefore, the speaker strained credulity and science in drawing the stated conclusions. !
, C. Weber gave as paper 10| a study of West German workers through 1974 which showed elevated SMR values for lymphatic and digestive cancers. This is the only study, which suggests an increase in lymphatic neoplasia. He did notj see the brain cancer elevation suggested by others. As Radike ported out in the later discussion (tr. p. 181), the elevations found i^ Germany and not in the other countries may be due to differences jin lifestyle.
AP00048799
-26-
D. Cooper presented the Results of the CMA-sponsored FEH study for the VC/PVC workers. He reported a suggestive increase in brain tumors that was not dose dependent, and it should be noted that this cohort also contains the grotip from the Waxweiler study which, if eliminated, would not produce even a suggestive increase in incidence. This ; fact points more toward a local situation than to a VC-associated cause. See also Landfigan's comments on this point at p. 185 of the transcript, and further discussion by Cooper on pages 188-191, and Tassignon on pages 191-192, who agree that there is no basis for association between VO exposure and cancer at other sites.
E. Beaumont analyzed the statistical power of some of the human epidem iological studies in ^>aper 12. He pointed out that the two largest studies, with the greatest power, were negative for other sites.
F. Paper 13, by Falk, described a detailed search by the CDC for all U.S. angiosarcoma cases over the 10-year period ending in 1974. None were found which could be traceable to exposure from living near VC/PVC operation^ or working in fabrication plants. Because of the tremendous publicity attendent upon angiosarcoma, it is certain that any cases since 1974 would have been announced, thus we now have a 16-year periodiin which no neighborhood cases have been seen.
G. Baxter reported in paper 14 a similar study in Great Britain with similar results, Thelonly liver cancer deaths associated with vinyl chloride are those of PVC production workers.
H. Chiazze presented a fbllow-up on the ORC-sponsored study of fabricator workers as paper 19. Further examination of the original data has confirmed that there have been no angiosarcoma cases among the fabricator employees, and that there is no significant elevation of relative risk for tumors at other sites. An original suspicion of elevated mammary cancer in females was investigated by a case control study and found not to be related to exposure.
I. Paper 20 by Molina was a mortality study of Swedish fabricator workers. He, too, foiJnd no statistically significant elevation of deaths from any causes among this cohort.
J. Tamburo discussed a prospective clinical study of 1200 exposed workers in paper 16. |He found that, of all the many blood and functional tests beind performed, only the GGT, SGPT, and ICO clearance tests had adequate sensitivity and specificity to be of practical value in determining early liver damage. The other tests now in use are either too insensitive or have too high a false positive rate tq be useful.
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-27-
V. Human Studies, Polyvinyl |Chloride
A. Seaton presented, as jpaper 21, the results of a study in Great Britain of a selected group of workers who had experienced long, high exposures to PVQ dust, primarily those from dispersion resin operations, which havje high respirable size fractions. One of three X-ray readers found a| slightly higher proportion of small opacities which correlated with! exposure in 50 of the 818 film. There was some correlation of loss of FEV-1 with exposure, but less than that which was due to smoking, or age alone. There were no frank clinical effects found in the |Study group.
His conclusion was th at dust exposures cause "pneumoconiosis in the sense that there are very minor changes in the chest X-ray in relation to the dust exposure, and that there is also a minor effect on lung function...u
B. Arnaud related the ca^e history of one man in paper 22. The patient had bagged an undisclpsed type of PVC for 23 years, and suffered from bronchitis related to smoking. His studies showed an accumulation of PVC. granules in phagocyte clusters, and the disease was therefore diagnosed as PVC-pneufnoconiosis. Studies of 60 other "strongly" exposed workers showed no abnormalaties.
C. Paper 23 by Mostrangelo discussed the examination of 731 workers exposed to undefined PVC dusts, generally well above the OSHA limits, and 485 exposed to monomer. Twenty workers, 16 of whom were smokers, had noticeable X-ray changes, classified as at least one perfusion. In 388 subjects an ILO classification of 0-1 was found, the lowest positive reading. Statistical analysis showed that 32% of these cases were explained by age, and 6% by exposure if age were held constant. Similarly, smoking could explain 70% and dust 9%, if smoking were held constant. Monomer exposure was not a factor. The author concluded that the "changes are mainly related to age and smpking habits, and the rate of exposure (to dusts) is minor."
D. Waxweiler discussed itk paper 24 a study of the plant mentioned above in the comments on the Cooper paper which had an excess of lung and brain cancers. The lung cancer excess was primarily of the undifferentiated large cell type. He found no relationship for these cases to exposure to specific substances, and in fact observed that many of the cases were in workers with very short job histories, and therefore very low exposures. He stated that for the lung cancer cases, chemical exposure "almost looked like a protective effect." He then speculated that the cause of the lung cancer could be ffVC dust, but could not establish highly
.' significant correlations with exposure levels or times.
In the subsequent discussion period, Greenberg (tr. p. 337-342) updated this study frdm its end in 1974. The exposure estimates were revised and strengthened, and the case histories for various tumors were compared ^gain to exposure with the following results:
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1) There was aipositive correlation between angiosarcoma cases and exposure to vinyl chloride, and also some of the catalysts used in the plant.
2) There was n<( correlation between the large cell lung cancer and cfhemical or dust exposures.
E. Lillis reviewed some |earlier papers on lung studies in workers on paper 25. In one study a preliminary review of the X-ray film of workers in two plants showed some 1/0 or 0/1 levels (ILO classi fication) of opacitiels that tended to increase with exposure. A third plant with lowelr exposures (VC and PVC were not differentiated) did not show this relationship. As Cooper pointed out in the subsequent discussion (tr. p. 343-3), this low level classification indicates very minor changes, such as found by Seaton. Lillis found age to be at least as important] a factor as exposure. In the second study Ljillis found that smoking history was much more influential than exposure; and the mechanism of the observed changes was "not at all cl earj.11 A survey of other literature on the subject of the effect of VC on the lung was prefaced by the statement that "the evidence in this respect is less striking, I'd say. There are a number of studies which point to the possibility rather than actually demonstrate a specific sequence of Events."
F. Wheeler, in paper 16, discussed the differences in the various processes for producing PVC, and emphasized the large differences in the respirable dust fractions. Resin made by the dispersion or emulsion process is the only product that produces a significant proportion of respirable particles.
In summary, there was no Evidence presented that could lead to the conclusion that PVC does hot still meet the conditions outlined by the ACGIH for "nuisance" dusts, e.g., no changes in the architecture of the air spaces, no collagen or scar tissue formation, and a reversible tissue reaction (see p. 5iof the 1979 edition of the TLV booklet by ACGIH).
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VI. Reproductive Effects of ^inyl Chloride
A. Johns presented her 1977 data in paper 26 which indicated that vinyl chloride may have a slight fetotoxic effect at very high concen trations such as 2500 ppm in rabbits and mice, but displays no significant teratogen ic effect, and reviewed several other papers in general agreement wit h this finding, including the fact that ethanol enhances the fetotoxi c effect.
B. Rice presented a literature review as paper 27, with no new data. He reviewed the differences between fetotoxins, teratogens, and transplacental carcinogens, and cautioned about too literal extrap olation from reproductive effects observed in rodents to the higher mammals. He then concluded that the Maltoni data showed vinyl chloride to be a transplacental carcinogen in the rat. He also cautioned that, in thpse cases where a material may-be a prenatal carcinogen, the danger period to the mother may well be before she is aware of pregnancy.
C. The entire presentation by Fabricant in paper 28 on mutagenic effects appeard to be based oh a misunderstanding of the subject. Her principal theme was t|iat, because vinyl chloride is mutagenic in i_n vitro bacterial tests, it is a human mutagen. This, of course, does not follow. The bacterial tests are screening tests for potential carcinogenicity, about which there is no doubt for vinyl chloride. Such tests have no relationship at all, necessarily, for the develop ment of inheritable gfenetic changes, which is the definition of mutagenicity. Many experiments, discussed in this symposium and elsewhere, have failed to produce any evidence of the mutagenicity of vinyl chloride in mammals. Similarly, chromosomal breakage or exchange In somatic cplls is not related to mutagenicity, per se. Damage must be done td the stem cells or to the ova or sperm them selves to affect the hext generation. Therefore, this paper offered no facts on its putative subject.
D. Hatch explored the statistical power of various studies on repro ductive effects. She found that the Infante Ohio CNS study was deficient in power, but that the negative CDC recheck of this report had adequate power to detect a significant effect, as did the CDC study in West Virginia, which also was negative. Similarly, the Infante Firestone worker study on abortions and miscarriages had design deficiencies that prevented its results from being accurate, while the similar negative Buffer study did have adequate power. Therefore, there are no acceptable studies which show a human repro ductive effect from vinyl chloride.
*
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VII. Incidence of Angiosarcoma Several statements were made by the final panelists which were incorrect. In particular, both Nicolson (transcript, p. 490) and Wagoner (transcript pages 495-496) stated that the incidence of angiosarcoma was increasing.1 The fact is that the incidence in the United States has been decreasing since a peak was reached in 1975-76, and that there have been no new cases reported since 1978. The attached table gives a chronology of the reported deaths from angiosarcoma for this country, and had Or. Stafford of ICI been permitted to present his proffered paper on his worldwide angiosarcoma registry, these facts would have been presented to the symposium. It is important to recognize that all of these deaths have occurred in persons heavily exposed occupationally; there have been none in fabricator workers or in the general population. Wagoner's incorrect interpretation of the Brady report has been discussed above. The two peaks of 1968-69 and 1975-76 correspond to the recognized latency period since the two major expansion periods of the PVC industry that occurred just after World War II and in the late 1950`s, when several new companies entered the industry. There has been no comparable influx of new cohorts or workers into the existing cohorts since that time, and thus, with the concentrated effort to reduce exposure which the industry undertook in the 1960`s as the rpsult of the discovery of the acroosteolysis problem, we can have confidence that the majority of the cases are behind us.
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Deaths from Angiosarcoma In the U.S.
VC/PVC Workers
Year of Deat)i
Number of Deaths
1961 1
1962
0
1963
0
1964____________
________ 1__
1965 0
1966 0
1967 0
1968___________
________ 3__
1969 2
1970 1
1971 1
1972 ________ 0_
1973
2
1974 1
1975 4
1976___________
________ 4__
1977 3
1978 2
1979 0
1980 (thus far)
________ 0_
Total
25
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-32VIII. Conclusions
The results of this symposium confirm, if any confirmation is needed, the carcinogenicity of vinyl chloride in humans to produce angiosarcoma of the liver* Insofar as carcinogenesis at other sites, or activity as a teratogeri or mutagenicity are concerned, results are negative. Evidence was added that there is a no effect level in animals and humans, from the work of Maltoni, Hehir, Chiazze, Falk, Baxter, and Molina. PVC dust has been shown to accumulate in the lungs, and to produce a "benign" effect on lung capacity that is less than the normal effects of aging, and far less than smoking. It meets the conditions established by ACGIH for nuisance dusts. There were no new data presented, nor any evidence that the present limits on vinyl chloride Or polyvinyl chloride dust are not protecting adequately the health of the exposed workers, and therefore, the general populace.
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