Document em05v6eDVomYreZXay5wEROJG
Court Upholds EPA's Decision On Vinyl Chloride |
By Stephen Webmiel
Staff Reporter o/The Wall Street Journal
WASHINGTON - A federal appeals
court, saying the Environmental Protec tion Agency has great leeway in setting clean air goals, upheld the agency's deci sion against tightening air pollution stan
dards for vinyl chloride. In a 2-1 decision, the appeals court said ,
that whenever the health effects of differ ent levels of air pollution are uncertain, the EPA may set air quality standards that take into account the cost to industry and the technological feasibility of com
plying. Environmental groups said the decision,
if upheld on appeal, will permit the EPA to weaken federal air quality enforcement ef forts. "It's hard to imagine a statute that is clearer than the Clean Air Act when it says that health is the only factor to be considered in EPA's standards,'' said Da vid Doniger, lawyer for the Natural Re sources Defense Council. The group chal- ;
lenged the EPA's handling of vinyl chlo
ride regulations. But the appeals court. In an opinion
written by Judge Robert Bork, didn't agree < that the law was dear. The court said that j because the benefits of setting lower levels . for vinyl chloride were unknown, the EPA 1 was entitled to consider factors other than ; public health, including a form of cost-ben- j
efit analysis. Vinyl chloride, a gaseous chemical used j
by Industry to manufacture plastics, is ; widely viewed as a cancer-causing sub
stance. In 1976, the EPA announced air quality
levels for vinyl chloride that industry was required to meet At the time, the EPA said federal law allowed the agency to set air standards that weren't way out of pro portion to Industry's cast In complying with -them.
The standards were challenged by envi ronmental groups, and while the case was
.pending, Jimmy Carter replaced Gerald Ford in the White House. The EPA agreed to settle the lawsuit by proposing tougher standards in June 1977.
But the tough standards were never made final. Last year, the EPA withdrew them and proposed returning to the 1976 regulations.' The Natural Resources De fense Council appealed to the federal ap- peals court in the District of Columbia. |
The appeals court relied on a 1984 Su-' preme Court ruling that said when a fed eral regulatory law is ambiguous, federal courts should give considerable weight to the decisions of the agency that enforces the law.
The section of the federal clean air law that calls for regulation of hazardous pollu tion is ambiguous and the EPA's decision to consider cost "was reasonable," the ap peals court said.
Judge Skelly Wright dissented, agreeing with the Natural Resources Defense Coun cil that the law "is as devoid of ambigu
ity ... as any statutory provision probably can be."
EPA officials said the ruling reaffirmed their view of the law. "We felt we had dis cretion in implementing this section of the law," said Charles Carter, an EPA assis tant general counsel.
But the Natural Resources Defense ; Council's Mr. Doniger said that when the
Supreme Court ruling "is taken to this ex- | treme. It's difficult to think of what Con- 1 gress could say to eliminate ambiguity." i He said the decision may affect other pending challenges to EPA standards for benzene and for radioactive air pollu tants.
Mr. Doniger also argued that the ruling conflicts with past decisions of the appeals court and said he probably will ask the full ll-member appeals court to review it.
U W - 13160
CHEMICAL MANUFACTURERS ASSOCIATION Record of Meeting
f :eivei
e- '96
URL 13761
Environmental Health Associates
Date: September 6, 1986 Time: 9:30 a.m.
List of Attendees:
Place: Environmental Health Associates Oakland, CA
William Gaffey Sally Cowles Donald Whorton Otto Wong Has Shah
Monsanto Company Shell Oil Company Environmental Health Associates Environmental Health Associates CMA
1.0
Dr. Bill Gaffey discussed comments received by CMA on the Epidemiology Study of Vinyl Chloride Workers draft report. Some of the comments made by Air Products could not be incorporated in the final report because they would require additional work not included in the scope of work for the current contract. Dr. Gaffey will prepare a written record of comments that could not be addressed for various reasons.
2.0
EHA will revise the draft report based on the comments received and will submit the final report by the end of September.
3.0 A-Panel meeting will be scheduled soon after the final report is received to discuss a future course of action.
4.0 The meeting adjourned at approximately 12:00 noon.
(xsirm
__ ,
Has Shah, Ph.D. Manager, Vinyl Chloride Program
CHEMICAL MANUFACTURERS ASSOCIATION
March 17, 1986
D^ar Vinyl Chloride Panel) and Research Coordinator Member;
DrI Brian BynSTtof ICI sent me the enclosed "Register of Cases of Angiosarcoma of the Liver Due to Exposure to Vinyl Chloride." Please note that the register is marked confidential, and therefore should be used for your internal purpose only. Also enclosed is an artile I received from Mr. John Barr on "Occupational Exposure and Brain Tumors."
Sincerely,
Has Shah, Ph.D. Manager Vinyl Chloride Panel
^
Enclosures
1%
Formerly Manulactunng Chemists Association--Serving the Chemical Industry Since 1872. 2501 M Street, NW Washington, DC 20037 ^Telephone 202^887-1100 Telex 89617 (CMA WSH)
Air Products and Chemicals, Inc. Be* 538
Allentown. PA 1QT05 Telephone (215) 481-4911
products z:
9i x n fl
27 February 1986
i
Or. Has Shah Chemical Manufacturers Association 2501 M Street, N.W. Washington, D.C. 20037
Dr. Roy Gottesraan The Vinyl Institute Wayne Interchange Plaza II 155 Route 46 West Wayne, NJ 07470
Sirs:
You may wish to bring the attached paper to the attention of your various committees Interested In vinyl chloride health effects. It describes VC as the only recognized central nervous system carcinogen.
Johtf'T- Barr, Maannaaggier Regulatory Response
JTB:pt>r 0608c
Enclosure: Moss, 3. Toxicol. Environ. H. 16 703-711 <1985)
OCCUPATIONAL EXPOSURE AND BRAIN TUMORS
Andrew R,, Moss
University of California, San Francisco, California
Epidemiological evidence of an occupational risk of brain cancer has been reported in four industries where chemical exposures are likely, most recenf/y in a series of prospective studies in the petrochemical industry. However, only in the case of vinyl chloride exposure has an occupational central nervous system carcinogen been iden tified. This report reviews the convergence of epidemiological and laboratory evi dence that established the occupational carcinogenicity of vinyl chloride, and dis cusses in detail the current evidence for an occupational risk of brain tumors in the petrochemical industry.
INTRODUCTION
Primary brain tumors of the glioma series, which make up about half of all brain tumors, show a male-to-female ratio of about 1.5 to 1. Brain tumors in general appear to be increasing in incidence among older cohorts (Waxweiler et al., 1983). Thus brain tumors in general, and glioma series tumors in particular, are sometimes considered as a priori likely suspects in the search for occupationally related tumors. Furthermore, gliomas can be produced experimentally in rats by at least four groups of experimental chemicals: aromatic hydrocarbons, N-nitroso compounds, triazenes,and hydrazines. More recently, brain tu mors including gliomas have been shown to be produced by inhalation in rats by three industrial chemicals, bis(chJoromethyl) ether, vinyl chloride, and acrylonitrile (Maltoni et al., 1982). These experimental results, together with the established history of brain-tumor carcino genesis in vinyl chloride workers, have led many researchers to lend at least preliminary credence to reports of brain tumors occurring in other industries where there are chemical exposures. Most recently, a series of studies have suggested excess risk of brain tumors in the petrochemical industry.
Evidence suggesting an excess of brain tumors has now been reported for at least four occupational groups: rubber workers (begin ning with Mancuso's investigations in the 1950s), chemists, vinyl chlo-
This research was supported in part by gram 1 R01 OH 01557 from the National institute tor Occupational Satety and Health.
Requests for reprints should be sent to Andrew R. Moss, Epidemiology and InuTn.i'miui Health, UCSF. San Francisco General Hospital, 995 Potrero Avenue, Bldg- W.ird 84 \in l mtv cisco, California 94110.
703
journal of Toxicology and Environmental Health 16:703-711, \w, Copyright C 1985 by Hemisphere Publishing Corporation
URL 13765
704 A. R. MOSS
ride workers, and petrochemical workers. However, the convergence of epidemiological and laboratory investigations that is usually ac* cepted as the informal criterion of proof in such situations has been hard to demonstrate (see, e.g., Cole and Merletti, 198C Doll and Peto, 1981). Thus, Mancuso's original observations in the rubber industry were not followed by the identification of any specific carcinogen, and the existence of an occupational risk of brain tumors in rubber workers is currently open to doubt (Mancuso, 1982; Symons et al., 1982). Braintumor risk in chemists has been shown only in a series of Swedish studies, and as yet no likely carcinogen has been identified (Olin and Ahtbom, 1982). The convergence of an epidemlologically identified risk and a suspected carcinogen has been demonstrated only among vinyl chloride workers. Thus Cole, in his surveys of occupational carcino genesis, recognizes only vinyl chloride as an established industrial brain carcinogen (Cole and Merletti, 1980). Doll and Peto, more con servatively, admit the brain only as a "possible" site of occupational carcinogenesis (Doll and Peto, 1981). The history of vinyl chloride as a central nervous system (CNS) carcinogen is discussed in the next sec tion.
Historically, the establishing of occupational or environmental risks has often been a complex and drawn-out process, sometimes requiring decades for the development of a consensus on a particular exposure. Thus although the issue of excess risks of brain tumors in rubber workers is currently in debate, the persistence of reports of brain tumor excesses in this and other industries has, as it were, promoted brain tumors to the top of the list of tumors that may be associated with important occupational risk (along with lung cancer, leukemias and lymphomas, primary liver cancer, and, more recently, melanoma). This was the situation in 1978 when a cluster of brain tumors was reported in petrochemical workers in Texas, initiating a major wave of research into the subject. The petrochemical research is also reviewed in this article.
VINYL CHLORIDE AS A BRAIN CARCINOGEN
Cole observes that occupational carcinogens are usually recognized because they generate an unusually high rate among a small exposed population, and because they produce tumors that are otherwise un usual (Cole and Goldman, 1975). Vinyl chloride (VC) is the classic case of a carcinogen that has such an effect, producing in workers exposed to high levels of the gas the very rare angiosarcoma of the liver (ASL). The first reported case of ASL in a vinyl chloride worker was diagnosed at the B. F. Goodrich company in Louisville, Kentucky, in May, 1970; the second in March, 1973; and the third, at autopsy, in December, 1973 (Heath et al., 1976). Since the incidence of ASL in the United States
OCCUPATIONAL EXPOSURE AND BRAIN TUMORS
705
was then 20-25 cases/yr, the appearance of 3 cases among a small group of workers prompted considerable concern. Furthermore, concurrent studies by Viola (1971) had shown skin, lung, and bone tumors in rats
exposed to VC by inhalation. {Viola's carcinogenesis studies were re portedly an outgrowth of his work on acroosteolytis in VC-exposed workers. Hepatitis-like liver changes had been reported as early as 1949 (Nicholson, 1977).J.
Following Viola, Maltoni demonstrated angiosarcomas in rats ex posed to VC in 1972 (Maltoni et al., 1982). This result was communicated to the Manufacturing Chemists Association, which following the dis covery of the third case at B. F. Goodrich, made public the finding of three cases of angiosarcoma in VC-exposed workers in the Wall Street Journal. With this announcement, a major effort began to study vinyl chloride workers, including a National institute of Occupational Safety and Health (NIOSH) follow-up study of 1294 workers with extensive VC
exposure in four plants. A concurrent histopathology study reviewed tumors reported on death certificates of all workers in the four plants.
The NIOSH study, published in 1976, showed very high relative risks in the category "biliary and liver cancer." The relative risk was 11 for workers with 10 or more years of exposure and 16 for workers with 15 or more years of exposure. Furthermore in the concurrent histopa thology study, 11 of 14 reported liver and biliary cancer cases on death certificates were ASL (Waxweiler et al., 1976). These observations have
remained the primary epidemiological basis for the assertion of the carcinogenicity of vinyl chloride.
However the study also observed a significantly increased relative risk for brain tumors, with 3 observed and 0.6 expected among workers exposed more than 15 years. At the same time Maltoni (1976a) reported that brain tumors as well as ASL could be produced in rats exposed to VC by inhalation. Furthermore the NIOSH histological study showed that 9 of 10 brain-cancer deaths in the VC worker cohort were glioblas toma multiformes (the most commonly occurring tumor in the glioma series). This proportion was thought to be unusually high. (However, it has been shown that the expected proportion of glioma-series tumors in such a series depends heavily on the number diagnosed at autopsy (Schoenberg et al., 1978)]. These results were sufficient for the devel opment of a reasonable consensus that brain tumors as well as ASL were associated with VC exposure. The primary evidence in the devel opment of the consensus was the correspondence between the human data and the laboratory inhalation studies, in which the exposure levels were thought to be close to human occupational exposures, (see, e.g., Wagoner and Infante, 1977). Vinyl chloride is the only occupational chemical carcinogen for which a correspondence exists.
Waxweiler et al. (1983) also note that in the 9 glioblastoma multi forme cases identified in the VC workers histology study, the average
706 A. R. MOSS
time since first exposure to vinyl chloride was 21 yr. Thus the epide miological observation of risk may have followed the oncogenic expo sure by a generation, and the circumstance of exposure could well have changed by the time the risk was recognized. This long latency period is characteristic of occupational carcinogenesis. The excess risk of mesothelioma in asbestos workers, for example is not generally ob servable until 20 yr after exposure (Selikoff, 1977). The long latency pe riod has important consequences in the case of brain tumors, which are not rare tumors.
The identification of VC-produced brain tumors, currently the only accepted example of occupational CNS carcinogenesis, offers some important lessons for studies of other industries. First, vinyl chloride was identified as a CNS carcinogen because it produces, as its primary effect, the extremely rare ASL. The excess risk of brain tumors would probably not have been recognized if it had not "piggybacked" on the rarer tumor. Second, the brain was only recognized as an additional site of carcinogenesis because comparable ranges of tumors were seen in human and animal inhalation studies. There is no other occupational carcinogen for which such a correspondence is currently known. Third, the number of tumors reported in the primary study was very small: there were 3 cases in the high-exposure cohort, and 10 in the concur rent histopathology study. Fourth, the period between initial exposure and observation was so long that observed effects may in fact have been archaeology rather than epidemiology--the carcinogenic situa tion may well have no longer existed when the excess risk was ob served.
BRAIN TUMORS ANO PETROCHEMICAL EXPOSURE
The intensive study of brain tumors in the petrochemical industry began in 1978 when as employee at the Union Carbide plant in Texas City, Texas, reported a newly diagnosed brain tumor to the local office of the Occupational Safety and Health Administration (OSHA). A joint -study with the Oil, Chemical and Atomic Workers union (OCAW) and company representatives identified a total of 10 brain-tumor deaths and cases among workers at the plant (not including the original com plainant, whose tumor proved to be metastatic). This number was suf ficient for the OSHA office to request a formal study by NIOSH. A joint study, with Union Carbide researchers, was initiated. A proportional mortality study of OCAW members in South Texas was already in prog ress, and additional studies in other refineries and chemical plants were initiated over the next year.
However, in 1979 both the Three Mile Island incident and the Fed eral declaration of emergency status for the Love Canal area took place.
OCCUPATIONAL EXPOSURE AND BRAIN TUMORS
707
and in the ensuing controversies over environmental carcinogenesis the atmosphere became polarized between industry and govern mental-union forces. As a result, competing industry and govern
ment-union studies were set up in several of the exposed petrochem ical cohorts in Texas and Louisiana. When a meeting was convened at the New York Academy of Sciences in 1980 to review the studies, a total of eight were presented, four from each group. The four govern mental-union studies uniformly indicated a twofold risk of brain cancer among petrochemical workers; the four industry studies uni formly failed to detect any excess risk. "To the innocent observer/' Science reported, "the crisp pattern of falling chips appeared at first sight to display blatant gerrymandering" (Lewin, 1980). It was also true, however, that the range of methods and cohorts involved was consid erable and that there was extensive methodological disagreement. Reeve et al. (1985) reviewed the issues. The primary methodological questions were (1>the tendency of proportional mortality studies, as carried out by NIOSH, to inflate cancer risk, and (2) the tendency of
industry-wide cohort studies, as carried out by the industry groups, to bury small groups of at-risk workers in very large cohorts. These issues were not resolved as, with the new Federal administration in 1981,
NIOSH capacity to continue the epidemiology studies was lost. With no pressure from the regulatory side, the industry studies appear to have slowed down also.
However, most of the proportional mortality studies were eventu ally converted to standardized mortality form, and a review of these studies is now possible. Savitz and Moure (1984) have recently reviewed the six prospective studies of refinery workers that were initiated by labor-governmental and industry groups in 1979-1980. Table 1 is
adapted from Savitz and Moure, with the addition of results from two studies of petrochemical plant workers, those of Waxweiler et al. (1983)
and Reeve etal. (1983). (One study, that of Thomas etal. (1982); remains a proportional mortality rate study (PMR): the others use standardized
mortality ratios.) All cohorts of petrochemical workers had low overall mortality, as
is generally the case in studies of "healthy workers," and six of the seven for which all-site cancer mortality or incidence were reported showed lowered total cancer rates. [The exception was the PMR study of Thomas et al. (1982).] However, brain-tumor rates were elevated in all but two of the studies, the exceptions being the refinery-wide study of Wen et al. (1983), which included salaried workers, and the industry wide study of the British petrochemical industry by Rushton and Alderson (1981). There was additional evidence of an association in more detailed substudies. Thus Savitz and Moure (1984) note that while Hanis et al. (1982) report an overall relative risk of 1.02 for brain tumors in their study of the Baton Rouge Exxon refineries, a more highly exposed
706 A. R. MOSS
TABLE 1. Relative Risk for Brain Cancer and Melanoma in Prospective Epidemiological Studies of Refinery and Petrochemical Workers*-*
All cancers
Brain
Melanoma
Study
RR N RR N RR /V
Theriault and Goulet, (1979)
Rushton and Alderson, <1981)
Schottenfeld et al. (1981) (mortality)
Schottenfeld et al. (1981) (incidence)
Thomas et a). (1982) (PMR)
Hants et al. (1982)
Wen et al. (1983)
Waxweiler et al. (1983)
Reeve et al. (1983)
0.89
25 3.90
3
0.89
1147
0.80
36 2.16
14
0.76
127 1.63
8
0.86
240 1-29
9 1.32 13
1.19
474 2.28
27 1.61
11
0.92 249 1.02 5
0.96
839 - 0.99 30 1.22 16
0.81 131 1.81 13
N/A N/A 1.09 25 -- --
* Adapted from Saviu and Moure (19841. * RR, relative risk; N, number.
subgroup had a higher risk, in the Reeve et at. study of Dow chemical
workers, while the overall relative risk was 1.09, the risk among workers hired before 1945 was 1.83 (Reeve et al., 1983).
On the basis of the first six studies, Savitz and Moore comment that there was reasonably consistent evidence of a potential association
between petrochemical exposure and brain cancer. The two chemical* plant studies appear to strengthen the association.
In an independent review of ail NIOSH investigations in eight in dividual refineries and chemical plants in Texas, Reeve et at. (1983) note
that inconsistencies remain in the piant-by-plant results, and that case* control studies within the studied cohorts show no consistent patterns of exposure. However the consistently elevated brain-tumor risk in the
prospective studies appears sufficient at least for this line of research to continue.
Savitz and Moure note that melanoma risk is rather consistently
elevated in the studies of petrochemical cohorts, as well as brain-tumor risk. This result is of interest because of an emerging pattern in recent studies of nuclear fabrication workers. Hadjimichaei et ai. (1983), in their study of the United Nuclear facility in Connecticut, observed rel
ative risks of 2.40 for brain tumors and 2.12 for melanoma, against an
OCCUPATIONAL EXPOSURE AND BRAIN TUMORS
709
all-sites relative risk of 0.88. Furthermore, Wilkinson et al. (1983) ob served a tripled risk of brain tumors at the Rocky Flats nuclear plant, and Austin (1981) observed a tripled risk of melanoma at the Lawrence Livermore laboratory... Attempts to explain these risks by radiation ex posures have proved generally unsuccessful; the similarity with the pattern of risk among petrochemical workers suggests that perhaps the cause is in some other aspect of the fabrication process.
CONCLUSION
Although this review suggests that the issue of brain tumors in pet rochemical workers is at least worth further study, most of the pro spective studies appear to have been dropped. However, a second wave of large case-control studies of occupational exposure in brain tumors has now been set in motion (see Table 2). In these studies, all brain-tumor cases or deaths in a specific case-finding area over a spe cific period are interviewed, either in person or by proxy. These large studies may eventually resolve the issue of whether there is a genuine
TABLE 2. Case-Control Studies Currently in Progress of Occupational Exposure in Glioma Patients
Investigator
Number of Number of
Source
Site
cases
controls
of cases
Location
Thomas, T. 1., NCI Environmental Epidemiology Branch
Preston-Martin, S., University of
Southern California Moss, A. R,,
University of California, San Francisco Buffler, P., University of Texas Ahlbom, A., Hudinge University Hospital, Sweden Musicco, M., Neurological Institute C. Besta, Milan
CNS CNS Glioma Glioma Brain
Meningioma/ glioma
600 300 500 650 350
800
600 Death certificate
New Jersey' Louisiana
300 Incidence
Los Angeles County
500 UC5F clinical
Northern
cases and death
California
certificates
870 Incidence
Coastal Texas and Louisiana
300 Clinical cases
Hundmge
in 2 hospitals
3.600
Hospital cases
Milan
* From Muir and Wagner 0962) and P. Buffler, personal communication
710 A. R. MOSS
excess risk in petrochemical workers. [However, Cole notes that such large case-control studies are only effective when the exposed group makes up at least 2-3% of the population studied (Cole and Goldman, 1975).] It should also be noted that while large case~controi studies of brain tumors may identify industry-wide risk, they cannot, by their na ture, identify the pattern of tumor sites associated with a specific ex posure. This latter information is generally accepted as important in establishing risk.
In conclusion, the prospective studies of petrochemical worker co horts reviewed here suggest that there is an increased risk of brain tumors associated with petrochemical exposure, possibly accompanied by an increased risk of melanoma. No evidence of a specific carcinogen has been established, and while the current generation of large casecontrol studies will probably identify any overall risk in the industry, these studies will not identify the pattern of sites at risk. In the light of the consistency between the petrochemical worker studies and the recent nuclear-fabrication worker studies, there is an argument for a coherent program of prospective research in these cohorts. Other studies that could usefully be coordinated with such a program include a review of the specific-exposure inquiries in the petrochemical worker cohorts, an examination of the change in the incidence of glioma series tumors among all brain tumors, and an exploration of other associa tions between brain tumors and melanoma.
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LIVER ANGIOSARQCMA GASES
awFimintf.
VPH/A3. - ASL ATDRESS
Q5CDLAITGN OF HEEISIER
ADAMS Dr ARoss Air Product*, Allentown, Pa, USA
BAGSHAW Dr IMM Norfllt Hydro, Newton. Aycllffe, IK
BAND Dr P R
rjiTvw Central Agenc? of British Colinhis, Vancouver, Canada
BARNES Jnr W C Monsanto, St Louis, Missouri, USA
BARR Dr J T
Air Products, Allentown, Pa, USA
BABRAlC Dr G
AECRF, Gocmsntry, France
BAXTER Dr Peter EMAS, Loodco, IK
BEAIFRE M
Govermnc of Quebec Cancer Registry, Canada
BENECHDr M.
Nephtachlale, Lavers, France
BEKCrr Dr B ia HUlhouse, IK
BEKEAZZI Dr P Inst of Occupational Health, Milan University, Italy
BESCTE Dr
Dynmait Nobel, Troladcrf, Gennany
BISSV Dr C
EMAS, Bootle, IK
BOBREUI F E Georgia Gulf, Delaware City, USA
0CTER R W
Fames* Plastics, Delaware City, USA
BJBGESS Mr David Id Anericaa, Wilmington, Dalnaats USA
SEEN Dr David Kemaoord, Stockholm, Sweden
CAKHR Dr J T DIAS, Lcndca, IK
CZLLA Mr C
Enichem Pol Imerl, Milan, Italy
CHANCE Mr M
Id Runcorn, IK
OAUS Mr P G
OASIOi Mr B
ARK, Bruaaela, TWijriw Norsk Hydro, Newton Aycllffe, IK
OTIAS90I Dr J C Chios Qdsrle, Saint-Tons, France
DAVIES Mr J G Id, Everberg, Belglta (2)
EE SLOWER Dr Solvay & Cie, Bnmaela, Belghae
DE VOS Mr A J Id Everberg, Belgium
DUE Dr HU B F Goodrich, Akron, Ohio, USA
DOLL Sir Richard Imperial Cancer Research Find, Oxford Univereicy, IK
DCMEBCWSa S L Dow Chemical, Mtdlmri, Michigan, USA
tmKTMrG
AAE, Brussels, Belghn
EMUNGER Mr H VKE, Frankfurt, Genmny
SBCI Dr V
Berufsgenoesenschaft dcr (hoischea Industries, Nurnbarg, Geramiy
FAIR, Dr H
Chronic Diseases Dtv, US Dept of Health & ftmen Selcaa, Atlanta, USA
FERGUSCNDr DM Id Aaezlcaa, WllalngtA, Delaware, USA
KSWANDrD
Inpeilal Cancer Research Fund, Oxford University, IK
ERASE R W
DlverslTech General, Akrai, Ohio, USA
ERJSXL Dr B P Bcrufegenpaaepecheft der Chesiechan Induatxlea, Heldelbfg, Germany
GOLERG Prof L Duke Univ Medical Center, Durham, North Carolina, USA
GOSZIOHI Jar Dr R E Teneco OmmLcals, Placafwey, Near Jersey, ISA
GCfnEEMAN R T The Vinyl Institute, New York, USA
HARRIS Dr W D Uniroyal Inc, Mlddlebury, Comarrlnm, USA
HUL Dr G B
Alberta Cmicsr Board, Edmonton, Canada
HH1MAN Dr D W Dlmncnd Shamrock Ccerp, Dallas, Tens, USA
HDDESER Dr R K_ BF Goodrich, Cleveland, Ohio, USA
HXGSCN Mr J
EMAS* Bootle, IK
BOGG Dr U A
Imperial Oil Ltd, Sarnie, Ontario, Canada
HOWARD Dr J K University of Otago School of Medicine, Wellington, New Zeeland
awHR? Dr N F Id Australia, Melbourne, Australia
JAWERT Mr J ' Chios Chlaie, Faria, France
JERVIS MrHR Id MUlbank, Lcnho IK
KAKRH Dr Bruca IXgioot, Wilmington, Delaware USA
XREl33t Dr R A BF Goodrich, Akron, Ohio, USA
LALOQC Dr J P Solvay, Bruesela, Belglua
IANRAK Dr John Dow Oiendeal Europe, Bergen, Switzerland
LAURENCE Mr J SPI, New York, USA
UMQ3KS-JQ1ES Sir telatophar. Chief fedlcal Officer, ICI, London IX
LES Dr F I
Victoria Hospital, Blackpool, Lancs, IK
LELBAffl Prof VK Univereity of Bonn, West Genamjy
LEVEQDE Dr G <EF Chlmle, AZF, Bullylea-Mlnaa, France
LEVISCN Dr D A St Berdn1nmew*e Boepltal, London, UK
LEWIS Dr P
(hadcal Industries Aasodaciaa, London, IK
URJVTER Mr
Solvay, Brussels, Belgrfia
LOSSAIO Dr J Atocham, Franoa
-2- WFX/ASL - A5I AECFESS,2
ltin
MAH1A8D Dr J K Medizinscha Abtellung, Lu2ern, Switzerland MALHCJIRA Anna Statistics Canada, Ottawa MA13CNI Prof C Institute dl Oocoiagla, Bologna, Italy
MAHKE Prof Lo Medil-Anic-S, Milan, Italy
MATT3BSSI Dr R Montedison, Milan, Italy
MTTDU7ICN D
Norsk Hydro, Newton Aycliffe, OK
M*XA Mr
Neste Oy, Espoo, Finland
MWIESAND Dr R IARC, Lyons, France
MOTT Dr A A EK^erial SAIC, Buenos Aires, Argentina
MJNN Dr A
Mxitanto, Brussels, ^g^--
HJtBZ Mxncxi Dr M Ri Bodsx>, Ifadrid, Spain MacSMEEN Prof KW Upstern Inflrnsry, Glasgow, Scotland
NAKAMJFA S
Japanese PVC Assoelatlcn, Tokyo
O'SULLIVAN Dr JJ IQ Sworn, W.
OLSON B G
VC Safety Association, Louisiana, USA
OMEN Dr R
Ifcadee Union CbngreM, London, tK
PA2XXE Dr G M IQ Central Medical Group, Alderley Parte, IK PAOLAIiaGA Dr S Montwileoa, Milan, Italy FOHTSt Dr Hans Haunt Sinai Medical Center, New York, USA
POSSBERG Dr J Wacker-Chanle, Mulch, Ornery
HJBS Dr A M TOHDHAM Dr J
Arochew, Brlgnoud, France Canettan Centra for Occupational Health A Safety, Hendloon, Canada
RAHSADD Dr J BP Racheichas, Antony, Fmcf
RAISES P BICHASD Dr P
Norsk Hydro, Pongrvnn, Norway Rhone Poulenc, Roussillon, Fmca
BDBSCN Mrs D Saskatchewan Cencer Foundation, Regina, Canada
RCGRIGUES Dr MTF ia, Seo Paulo, Brasil
ROUSH Dr G
Monsanto, St Louis, Missouri, USA
RDTY Dr J
Atochen, St Aubsn, Prune
SALE Dr J
NIOSH, Cincinnati, USA
SARA0Q Dr R IARC, Lycos, Franca
SOEFFESS Dr ML 1)94/090, Geleen, Holland SCSIEFER Dr H University of Manitoba, Winnipeg, Canada
SERCttE Dr D Dianood Shaarxk, Dellas, USA
SHAH Dr Ess
(MA, Wrthiagwn W, USA
SXGRIST Dr J Shell Otdflde, Berra L'Etaog, Frame
9H!H Dr C
Division of Envlrcunancal Health, World Health Organisation, Geneve, Switaetimd
SMQH Dr P M Llandough Hospital, Penarth, UR
SFIRXAS Dr R NQ/N2H, Betheada, MaryUni, USA
STAFKRD Dr J Saesrset, IK
SIABERER Mr BASF, Lndwigshefon, Gstaany
TttfflUBBD Prof CH University of Louisville, USA
TER HAAR Dr Gary Ethyl Corporation, Baton Rouge, touts!ana, USA
TCHflESCH Dr B Chendecbe Wsrrt Hula, Kxels Rsrk.1 inghaueen, Gemny THERIMI.T Dr Gillee MaGlll Uni-varsity, Montreal, Cmeda
TfflKSS Prof Dr AM BASF, LukdgsNiafen, Gacwny
1HIIS-EVBQCN DC. E Honk Hydro, Focagrunn, Ncrtvy
TH9PSGH Dr D H Oncer TTaaaant 6 Research Inundation,
Nova Scotia, Quads
TUDOIR Dr V Shall, An Dm Bag, Holland
VAN DSR msm Dr S J Aid, Sasdburg, Sotih Africa
UAXLMZ J R
Esso, Sarnia, Ontario, Canada
WA12EMH3S H ~ BF Goodrich, ClavaUnd, Ohio, Da
VETOING S 0 Renamed, SeockhcOa, Sweden
UEELER Dr D J IQ Blllna, IX
UBEZZR R N
Uhlan Carbide, South CUrlestcn, USA
WISIGN Dr J
ia Hlllhoiae, IX
WHng X R WHJN9CI 0
Dupexial, Buenos Alias, Argentina EXectroehsaical Industries, Acre, Israel
vmiAtfi Dr IMJ BP Owicals, Peoerth, IX
VILSCN Prof R Harvard University, Cartridge, Massachusetts, USA
WIGHT Dr A P IQ Wilton, IX
YCS& J
IQ Everberg, iwigtf
Frees Dr B Bemetx, Medical Department, Imperial Chemical Xaduatrise Pic
Rlllhouee Site, PO Bccc 4, ThorntotrClcveleys, Blackpool FY3 4QD, IX.
February 1986
CONFIDENTIAL
REGISTER OF CASES OF ANGIOSARCOMA OF THE Lira DUE TO EXPOSURE TO VINYL CHLORIDE - REVIEW DATE 1 JANUARY 1986 PREFACE s Acknowledgments, significant changes and concents
1* The new esses In the Register are the following :
France Gsrmany UE
18 23, 24, 25, 26, 27 11, 12
2. There are amendments from the previous Register against the following cases:
Germany 21, 22
US 36, 38
3. I would like to thank Dr De Sloover, Dr D M J Williams and Dr Friedel for informing me of new cases.
4. For the case corrections I would like to thank Dr FTiedel, Mr J T Barr and Mr B W Frame.
5. For other corrections and information, thanks to Dr D Fornan, Mr J T Barr, Mr T H Sutherland and Mr N F Humphry.
6. I should be very grateful if all recipients of the Begister could continue to keep me fully informed of any new cases, or, if they should hear of other Companies who have acquired a case of ASL, it would be much appreciated if I could be notified by the appropriate person.
It is extremely helpful if new information is supplied in tabulated form, using the headings in the Register as far as possible.
7. I would like to thank the many people who have suggested research topics, and should be grateful if I could be kept up to date.
8. I shall be happy to supplyto any recipientof the Register a copy of the Paper "Exposureto VinylChloride
andAngiosarcoma of theLiver:
a report of theRegister of cases" by Dr David Forman,myself. DrJohn Stafford
and Sir Richard Doll, published in the British Journal of Industrial Medicine, November 1985 (42: 750-753)
Dr Brian Bennett
Medical Department
Imperiel Chemical Induatries pie Uillhouse Site P 0 Box 4 Thornton-Cleveleys Blackpool FY5 4QP England
February 1986
sue nan
Index
Table Sentience Belglua
1
Canada
Czechoslovakia
France
Ceraany
Italy
Japan
Norway
Sweden
UK
USA
Yugoslavia
Incidence of Cases per annua (Table 1)
Distribution of Cases
by Country
(Table 2)
Pattern of Cases by
Factory
(Table 3)
Latency Periods (Table 4A)
Distribution of Latency Periods (Table 4B-4H)
Annual Geographical Incidence (Table 5)
IMPERIAL CHEMICAL INDUSTRIES PLC LIVER ANGIOSARCOMA CASES (REVIEW DATE - 1 JANUARY 1986)
WPX/ASL 2 - LANGI0CASES,4
Page i 2-3 4 5-8 9-14 15 16 17 18 19-21 22-28 29 30
31
ASL Case Nuabera by year of Death (Table 6)
ASL Case Nuabers by year of first exposure (Table 7)
Western Europe PVC Producers - Start-up Dates vs ASL Case8 (Table 8)
USA PVC Producers - Start-up Dates vs ASL Cases (Table 9)
Canadian PVC Producers - Start-up Dates vs ASL Cases (Table 10)
East European PVC Producers - Start-up Dates va ASL Cases (Table 11)
Japanese PVC Producers - Start-up Dates vs ASL Cases (Table 12)
South 6 Central American PVC Producers - Start -Up Dates (Table 13)
Australasian PVC Producers - Start-up Dates (Table 14)
Pafie 42 43 44 45+46 47 48 49 50 51
32
33 34-40
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Page
31
Distribution of ASL Cases by Country
TABU_________ 2
(Review Date - 1 Jan 1986)
USA W Cereany France UK Canada Sweden Yugoslavia Italy Czechoslovakia Japan Belglu* Norway
35 *** 26 ** 18 ***
11
10 5 ****
4 ***** 4* 2
2 2 1
Total
120
* OnIt ItOl - atypical case of PVC bag extruder. ** Includes GE03 aerosol can filler. *** Includes case US 24 which was dlagnosad as Cholangiosarcooia 6 US 33, **** includes one aonoarr worker. ***** includes two nonoaer workers.
and 36;
and P 15 who are alive.
l.e Western Europe North Aaerlca Rest of World
67 45
8
WPX/ASL 2 - LANGIOCASES,36
Total 120
i.oeenn
I
Pattern of ASL Cases by Factory
TABLE 3
view Date - i Jan 1986)
(a) W Europe
Of the 67 caaes In W Europe, 57 have occurred In dusters at 11 factories. Of the 26 German cases, 23 have occurred In clusters at 4 factories.
ASL Cases
Dynamic, iTrolsdorf, Germany Chios Chinie (Formerly RP), St Pons, France BP, Berry, UK Wacker, Burghausen, Germany Kemanord, Sundsvall, Sweden PCUK, Brignoud, France CWH, Marl, Germaoy 1CI, Hillhouse, UK Solvay, Tavaux, France Lonsa, Ualdshut, Germany Solvay, Jeneppe, Belgium
11 8 8 7 5 5 3 3 3 2 2
5T
NB: There are 32 pre 1962 PVC plants In W Europe; 18 of these have had ASL cases (Ref Table 8)
(b) N America
Of the 45 caaes in N America, 38 have occurred at four factories out of a total of 54 factories:- In N America 43 plants have not had ASL cases.
ASL Cases
BFG, Louisville, US BFG, Shawinlgan, Canada UCC, S Charleston Goodyear, Niagara
14 10 10
4
38
NB: There are 28 pre 1962 PVC plants In N America; ll of these have had ASL cases (Ref Tables 9 A 10)
(c) Rest of World
The 8 ASL cases are believed to be In 1 cluster of 4 and 2 clusters of 2 cases.
WPX/ASL 2 - LANGIOCASES,37
8Q8VW
Page 33
TABLE 4A
(Review Date - l Jan 1986)
Latency Periods (Tears from first Exposure to Diagnosis)
Country
No of Cases
Total Years
Average
H Europe
Belgium
2 35 17.5
France
i
Germany
IS 459 25.5 * 26 495 19.04 *
Italy
6 74 18.5
Norway
1 22 22
Sweden
5 122 24.5
N America
UK
11 254 23.09 *
6T 1461 21.80
Rest of Uorld
US Canada
35 886 25.31
10 204 20.4 *
45
1090
24.22
Summary
Csechoslovakla Japan Yugoslavia
W Europe N America Rest of World
2 2 4 8
67 45
B 120
30 39 85 154
1461 1090
154 2705
15.0 19.5 21.2 19.2
21.80 24.22 19.2 22.54
Of the countries with > below world average.
WPX/ASL_2 - LANGIOCASKS,38
caaes> France, UK and USA have an average latency period above world average, Gernany and Canada
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WPX/ASL 2 LANGIOCASES,39-
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Page 35
TABLE 4C
(Review date 1 January 1986)
LAfAwCY_PERIOD OF ASL CASES TABULATED BY YEAR OP FIRST EXPOSURE
MAX POSSIBLE LATENCY PERIOD
YEAR OF FIRST EXPOSURE
LATENCY PERIOD (NO OF YEARS)
ARITHMETIC MEAN OF LATENCY PERIODS
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1939
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30,35
39 7 29.24,29.28
38 8 28,24,34
9 1950
30,26,20 26,22,31,19,23,14,33
458 - 24.11
IT
1 19.28,17,28
34 2 21**,15
33 3 25,42,23,22,20,31,22
4 21,21,25,25,21,28***,
22 725 - 21.97
5
22.23,24,14,19,21,27
"37
27*** 24,28
6 21,12,27***
29 7 19.17,15.13.16,28
28 8 18,18,15,17,20
9 16,21
368 - 16.73
1960
13,18,21
22
1 15,16,16,16,19,19,12 24 2 13,18.17,12.18
23 3 16,17,20,21
4 16,17
180 16.36
5 11,19
11
6 9,18
19 7 16
18 6
9 13
13
1970
VIOLA
14 2
ii 3
4
TOTAL
126 CASES
MALTON1 GOODRICH 2706 - 22.55 '
* Cholanglosarcosa ** Aerosol can filler *** US33 and 36; and P15 still alive.
WPX/ASL_2 - LANGIOCASES,40
URL 13811
TABLE 4p
Page 36
(Review dace 1 January 1986)
LATENCY PERIODS OF ASL CASES TABULATED BY YEAR OF FIRST EXPOSURE AND GEOGRAPHICAL
LOCATION
''
MAX POSSIBLE LATENCY PERIOD
47 46 45 44 43
39 38
34 33
29 28
24 23
19 l6
YEAR OF FIRST EXPOSURE
VIOLA
1939 1940
1 2 3 4
5 6 7 8 9 1950 1 2 3 4
5 6 7 8 9 1960 1 2 3 4 5
6 7 8 9 1970
LATENCY PERIODS IN
WESTERN EUROPE
NORTH AMERICA
38*
37,41
38 28 27 21,29,31,33 29 28,34 30,26 26,22,31 19,28 21** 25,22,22 21,21,25,25 22,23,24,27***24,28 21,12 19.17,15,13.28 18,18 16,21 13,18,21 15,16,16,16,19,19 13,18,17,18 16,17,21 16 11,19 9,18 16
21,37 32,38 14,32 11,24,20,24,34,39 22,28,29 26,28,15,23,30,35 24.29,28 24 20 19 17,28 15 23,31 21,28*** 14,19,21,27 27***
15
12 12 20 17
13
ROW
23,14 2i,i o 22 16 17,20
2 MALTONI 3 TOTAL CASES
6?
45
8
* Cholangioaareoaa ** Aerosol can filler *** US33 and 36; and F15 still alive
WFX/ASL 2 - LANGIOCASES,41
TABLE 4g
Page 37 (Review date 1 January 1986)
PLANT
START UP DATE
LATENCY PERIODS OF ASL CASES IN SPECIFIC PLANTS (10 OR MORE CASES)
NO OF CASES
AVERAGE LATENCY PERIOD
LOUISVILLE USA
SHAWINXGAN CANADA
S CHARLESTON USA
TROISDORF W GERMANY
1940? 1941? 1939? 1954
12,14,15,19,19,20,24f27 f28,28,28,29,29 31 11,12,14,21,22,23,24,24,26,28
24,30,32,32,34,35,37,38,38,39
12,13,16,16,18,19,19,21,23,25,28
14 10 10 11
23.07 20.5 33.9 19 .09
WPX/ASL 2 " LANGI0CASES,42
Page 38
TABLE 4g
(Review dace 1 January 1986)
LATENCY PERIOD OP ASL CASES TABULATED BY YEAR OF FIRST EXPOSURE AND SPECIFIC PLANT (10 OR MORE CASES)
YEAR OF FIRST EXPOSURE 1939 1940 1 2 3 4
5 6 7 8 9 1950
1
2 3 4
5 6
7
8 9 1960 1 2
S CHARLESTON USA
LOUISVILLE USA
37 32,38 32 24,34,39
30,35
20 28,29,27
29.28 ik
19
15
31
28 14,19
* 12
SHAVINICAN CANADA 21 14 11,24 22 26,28 24
23
12
TROISDORF
W GERMANY
21,25 23,28 12 13 16,16,19,19, 18
URL 13814
WFX/ASL_2 - LANGXOCASES,43
Page 39
TABLE 4G
(Review dace 1 January 1986)
PLANT
START-UP DATE LATENCY PERIOD OF ASL CASES
NO OF
IN SPECIFIC PLANTS(4-9 CASES) CASES
AVERAGE PERIOD
SUNDSTALL SWEDEN
1945
16,19,27,29,31
5 24.4 yeare
BRIGNOUD FRANCE
ST FONS FRANCE
1950 1939
11,16,18,26,30 21,28,29,37,38,27,41,35
5 20.2 8 31.88
BARRY UK
1948
9,17,18,28,31,33,18,19
8 21.62
BURGHAUSEN V GERMANY
NIAGARA USA
1933 1947
17,21,22,25,24,13,21 15,17,21,23
7 20.43 4 19
SPLIT YUGOSLAVIA
1941
20,20,22,23
4 21.25
WPX/ASL 2 - LANGI0CASES,44
Page 40
TABLE 4H
(Review date 1 January 1986)
LATENCY_PER10D_0P ASL CASESTABULATED BY YEAR OP FIRST EXPOSURE AMD SPECIFIC PLANT
(4-9 CASES)
YEAR OF FIRST EXPOSURE
1939
SUNDSVALL SWEDEN
BRIGNOUD FRANCE
ST FONS FRANCE
BARRY UK
BURGHAUSEN NIAGARA
W GERMANY
USA
SPLIT YUGO-
SLAVIA
1 2 3 4 5 6 7 8 9 1950 1 2 3 4 5 6 7 8 9 1960 1 2 3 4 5 6 7 8 9 1970 1 2
27* 31 29 19
16
26,30
37 38
29 28,34
21 18 16
11
_
31,33 28
25 21 22,24
17
21
18 17
19 18
13
15,23
23* 17
20 22* 21 20
-
* Monomer workers
VPX/ASL_2 - LANGIOCASES,45
Page 41
TABLE 5
(Review Date ~ 1 Jan 1986)
Annual Incidence of ASL Cases (Date of Death) by Geographical Area
1955
i
1961 2
4
7
8
9
1970 1
2
3
4
5
6
7 8 9
1980
1
2
1983
1984
1985 TOTAL
t
Western Europe
1
1
l
1
4 1 i 6 6 6
1
* 6
i
i
6 4 2
North America
1 1
1 l l
5
2
1
2
1
4 2
4
r T 2 4 0
l
3 1
J3**
Rest of World
1
3
1 i i! -
-
-'
8
Annual Total
1 1 1 1 2 1 5 3 2 3 5 8 5 11
ll
9 10
5 10
5 2 9 5 2 117
Cuaulatlve Total
Key Events
1 2 3
4 6
7 12 15
17 Viola 20 25 33 Haltonl 38 Goodrich 49 60
69 79
64
94
99 101 110
115 117
Includes G03 aerosol can filler but oalts It 01 bag extruder ** Does not Include US33, and 36; and F IS* All still alive*
WPX/ASL_2 - LANGIOCASES.46
^8nan
?age 42
TABLE 6
(Review date 1 January 1986)
ASL CASE NUMBERS BT YEAR OF DEATH AND GEOGRAPHICAL LOCATIONS (EXCLUDING IT01)
KEY EVENTS
WESTERN EUROPE
NORTH AMERICA
REST OF WORLD
Viola
Maltonl Goodrich
1955 6 7 8 9
1960 1 2 3 4 5 6 7 8 9
1 2 3 4 5 6 7 8
9 1980
1 2 3 4 5 Total
FI
G1 Swl G2 NUSw2.UKl.lt2 G3** * G4.G5.UK3 l03G6C7,G8,It3
B1 ,F4,F5 ,F6 ,F7 ,Sw3 F8,F9,G10,GU,C12,Sw4 F10.F11,G9,G13,G15 C16.G17 F12,F13,UK4,UK5,G18 UK6, UK7,G19,Sw5,G20,G2l It4,F14,UK8,G22,G23 G26 UK09,It5,Fl7,B2,G24,G25 UK10, F16, F18, G27 UK11. OKI2 66
Cl C2
OSS C3
US5 Cr2
C4,C3,US4,US7,US10 US12.US16 US11 C6.US2
C7 C8.US1.US3.US23 C9.US13
086,089,0818,0826 US19,US20,US22, C10,US21,US24* US27.US28
Tl.T2.Csl
Japl Jap2,Y3
T4
US17, 0S29, US30, US3. !
US31 US35. US34, 0S38 OS37
43***
8
* CholangloaareoM ** Aerosol *n filler *** Doss not include US33, and 36$ and F15.
All still alive.
URL1381B
WPX/ASL 2 - LANGIOCASES,47
Page 43
TABLE 7
(Review date 1 January 1986)
ASL CASE NUMBERS BY YEAR OF FIRST EXPOSURE ASP GEOGRAPHICAL LOCATION (EXCLUDING IT01) --^
KEY EVENTS
WESTERN EUROPE
NORTH AMERICA
REST OF WORLD
Viola Kaltoal
1939 40 l 2 3 4 5 6 7 8 9 50 1 2 3 4 5
6 7 8 9 60 1 2 3 4 5 6 7 8 9 70 1 -2
i
Frll,Frl6
Frl4 UKl Sw2 Frl,Fr3 Sw4 Sw3 Fr9t Frl7 Frl2,Fr4 Fr7,Nl,UK8,tJK9 Swl ,UK5 G3** G15,It3,G26 G7 ,G8,UK4,G19 Gil,G16,G18, Frl5*** G23.G28 FRIO.Gl Pr8,G4,It2,G2,UR12 Tr6,B1 Fr2,It4 G5.G13,G25 G9,010,612.017.G20.G22 G6,UK6,G2l,B2 Frl3, UK7,Frl8 Sw5 FrS.UKll UR3, UK10 It5
G24
US24*
C3.US27
US13, 0S29
C2.0S19 Cl tC5 ,DS5,US7,US28,US35
C4,US3,US9
C7,C9,US8 ,USU ,US21 ,0S3l
C6.US22US26
US1 0S12
US16
Y2, C*2
US10, 0S32 USA
CIO, US37
Japl,Y1
US18 ,US33***
T3
US2.CS17,US20,US34
US36*** US23
Cal Jap2,T4
C8 US6 US38 US30
Total 67
45
8
* Cholanglotareoma (US24) ** Aerosol can filler (G3) *** US33 and 36; and Fr 15 are still alive.
URL 13819
W?X/ASL_2 - LANCIOCASES.48
Page 44
WK/ASL_2 - LANSIOCASES.49
(Review dace 9 January 1986) TABLE 8
WESTERN TOCTE PVC PBOXJCZRS ~ STABX^IP PETES y ASL CASES (CHTTEDC G03 & It.01)
URL 13820
START-UP COCNIKT NAME CCHPANY N YEAR
1931 West Genueuv BASF
LOCATION Ludwigshafen
ASL CASE -UMBEL
YEAR OF
1 1st Exposure i
1933 West Germany Wacker
Burghausen
04.07.11.15.23.24 25157.54.55.53.55.69.601
1938 Italy
tontecatlni
Acna
1939 France
Rhone Poulenc St Pons
03.09,10.11,14. 46.48.56,41,43.
15.16,17
35,41,46
1940 United Kingdom ICT
Runcorn
1940 United Kingdom ia
HUUouse
01,04,12
44,54.57
1945 Sweden
Kemenord
StndsvallCStockvik)
51.45.47.46,64
Switzerland Loaza
Sins
1946 1&7
1948
France
Khonc-Poulanc
Italy
Mrotediaoo
United KtnorVTM BP Cham
ftxmillcn Porto Marghera Barry
01 02
46 57 66.51,62.63.50.50
10.11
!<*.
West Germany
Marl
09.10.26
!61.61,53
1949 Belsdm
Solvay
Janeppa
01,02
58.62
1950 France
Puk
Brianoud
02,04.05.06.12 59.49,65.58.49
France
Rhcne-Poulenc St Aubsn
oJ
50
Holland
Shell
Persia
Norway
Norsk
Berova
01
So
1951 Italy
Montedison
Brindisi
1952 Italy
Montedison
Teml
1$55 Austria
Halvic
Halleln
France Italy
Solvay Solvay
Tavmnt Ferrara
08,13,18 65
57.63.63 55
Spain
Rio Rodmo
Hemeni
!
United Kingdom BIP
AvdLiffe
Wbst Germany Hoectwt
Ggjdorf
18
55
1954 i West Germany Dynamit
TruLsdorf
01,02,06,12,16, 1 56,57^,6135.61,
17.19,20.21.22.27 54.61.62.61.55
1955 Spain
frfcnsanco Iberia Monzon
1956 Spain
Caiqsa
Sabinanigo
Hlspevlc
Torrelavega
1956 West Germany Solvay
Rhelabarg
1960 Italy
S C Ravens
1960 West GsrxDsny Lanza
Ravenna Waldstut
64 06.13
1 56 ! 627S5
1&2 Portugal
Clres
Oporto
1965 Franca
Bhone-Poulanc Mantlucon
Italy
Fozzi
Ferrandlne
Weat Germany Wacker
Cologne
1966 West Genanr H06SK
KnapaackCFrankfurt) OS*
60
1967 Franca
A30 Qdaie
Bel an
Spain
Rio Rsdano
Miranda da Ebro
Greece 1968 Belaiifl
Eaao Pappas Badiphil
Dlavata Salonika Antwerp
i
1969 United Klwden Vinataz
Italy
Riwfenr*
Staveley Cagliari Sardine 1
|
1970 Italy
SIR
Porto Torres Sar
United Kingdom ia
Runcorn
1971 Italy
S C Havas Ravems
Spain
Hlspevlc
Martorell
Sweden
Kanenord
Stamngsind
United Kingdom ff Cham
Bag!an Bay
1972 Flnlari
Pekena
Svartbeck
Holland
E6M
Bfidt Limburg
1976 France
Soc Art D'vlnyl Mazingarbe
19^ Spain
Maneante Iberia Tarragona
* Laboratory worker in P* --arch Department
PA16AC, Mira Venice, caee not J^-i***-- (it 05), due not knowing start up date of the Plane.
Page 45
TABIE 9
(Review dace 1 January 1986)
USA P?C PRCPPCSS - START-UP DATES v ASL CASES
SIAKIH3P OCMPANY Ntt YEAR 1939? *uoc
LOCATION S Charleston
ASL CASE
YEAR OF
NUMBER
1st exposub
07,13,19,21,24, 44,42,43,46,39,
27.28.29,31.35 41.44,42,46.44
1940? *BEG
loulsvllls
01,02,03,04,05, 48,55,45,52,44,
06,09,16,17,22, 62,45,50,55,47,
26.33.34,37
47,54,55.53
1946? *UCC
Texas City (Partially closed 1977)
1$4J Goodyear
Niagara Falla
08,10,11.20 46.5l.46.55
i44a Firestone
POttStOMQ
12
Unlroyel
Palnesvllle
(dosed 1975)
1950 Monsanto
Springfield
32
5T
(Closed 1975
1952 Dow
ttldlad (No PVC since c 1975)
BEG
Avon Lake
118
54
1953 SPG
Deer Park (Formerly Diamond)
1954 General Tire
Ashtabula
|36
54
1956 Air Produces
(dosed 1984) Pensacola
l
Atlantic Refining Brooklyn(dosed late 1960s)
Bordei
Leominster (dosed 1984)
Conoco
Bebtoctvllle (dosed 1975)
BEG Niagara
Great American
Fitchburg
25
58
Plastics
(dosed 1983)
Hooker
HleksvUle (dosed 1980-81)
Pautoeoco
Paaalac (dosed 1984)
1957 Atlantic Tubing Cranston (dosed 196?)
Teineco
Flaaingtoa NJ
130
59
1958 Kevsor Century
Saugus. Cal
I960 BEG
Weteon, Cal
Air Producta
Calvert City
;38
63
(closed March 1982 Da opened Octalter 1963)
Borden
1962 Tenoeco
Burlington SJ
1963 Couoco
Aberdeen. Miss
Stauffer
Long Beach. Gal (dosed 1962)
1965 Conoco
** Assonet. Mbss (dosed by OUn 1975. see below)
Ethyl
Baton Bourn (Closed 1984)
1966 Oorrla Gulf
Dalwmra City (Formerly Diamond) |
General Ttre/Pmcaa It Pleasant WVa (dceed 1963) 1
BBS
Henry. Ill
_______J________
Stauffer
Delawsge City (Sold to Formosa 1983)
196? Allied
*** Palnesvllle, 0 |
(sold to Robintedi)
Hooke
Burlington NJ
1
1968 Firestone
Perrwille (Closed 1982)
1969 BEG
Pedrlckton NJ
Goodyear
Plaouemine
Olin
** Assonet, Mass (dosed 1975) (See above)
1971
(Formerly Conoco) Oklahoma City Conoco
|
1
URL 13821
WEX/ASL2 - UK3DGASES50
Continued
TABLE 9 (Continued)
PSA PVC PRODUCERS - START-OP PATES vs ASL CASES
START-UP YEAR 1972 1973
COMPANY NAME
Nat Starch Borden Roblntech ***
1974
1975
1979 1983
Atlantic Tubing/ Tallvrand Shlntech Certain-teed Georsla Pacific Tenneco Firestone Formosa
LOCATION
ASL CASE
NUMBER
Meredosla. Ill
Springfield
Painesvllle, 0
(sold to Georgia
Pacific who
converted to polystyrene)
Cranston RI (ClosetH552)
Freeport, Tex Lake Charles Plaauemine, La Pasadena, Tex Plaquemine Point Comfort, Tex
YEAR OP 1st EXPOSURE
* My databank hae no information on UCC before 1946 or BEG before 19S0
** Refers to same plant at Asaonet
***Refer to same plant at Painesvllle. Allied plant never operated again for PVC after it was sold to Roblntech.
NB Some of the plants In this list were closed down, soma have changed ownership over the years, some have changed their product*
WFX/ASL 2 - LANGI0CASES51
Page 47
TABLE 10
(Review dace 1 January 1986)
CANADIAN P?C PRODUCERS - START-UP DATES vs A.SL CASES
START-OP TEAR
COMPANY NAME
1943 (1941?)
Goodrich
LOCATION Shawlnlgan
ASL CASE NUMBER
YEAR OF 1st EXPOSURE
01,02,03,04,05 44,43,41,45,44, 06,07,08,09,10 47,46,61,46,53
1951
Monsanto
La Salle (Closed 1! 75)
1957
Goodrich
Walland
1966
Esso
Sarnia
1979
Diamond Shamrock Alb Fort Saskatchewan
URL 13823
WPX/ASL 2 - LANGIOCASES ,52
Page 46
(Review date 1 January 1966)
TABIE 11
EASTERS BLOC PVC FACTORIES - START-UP DATES vs ASL GASES
START-UP COUNTRY NAME COMPANY NAME
TEAR
Pre 1939 East Germany State Comoanv
1941 Russia
State Coons
1950 Yugoslavia
Jugo Vlnil
1951 Czechoslovakia State Comps
1955 East Germany State Comns
T5T6 Rumania
State Comps
1957 Poland
State Comps
Rumania
State Comps
1956 1959 1961 1963 1965 196? 1969 19^0
1972 1975
1976 1977
Rumania
State Comps
Hungary
State Comps
Rumania
State Comps
Yugoslavia
Ohls
Bulgaria
State Comps
Poland
State Comos
Russia
State Comps
Rumania
State Comps
Russia
State Comps
Yugoslavia
Vlnllolastika
Czechoslovakia State Comps
Russia
State Comps
Yugoslavia
Hip
Rumania
State Comps
LOCATION
Schopau Vladimir et al Split Novakv Bltterfeldt Icechlm Osweiclm (Dvorv) Tlrnavenl Turda Rlsnov Barents Borsod Borzestl Skople Varna Tarnow Dlerllnsk Rlmnicti Vilcea Volgograd Zadar Neratovlce Raluah Area Pancevo Rlmnicu Vilcea
ASL CASE NUMBER
01.02.03.04
01.02
YEAR OF 1st Exposure
53.^0.54.48 57.50
URL 13824
WPX/ASL 2 - LANGIOCASES.53
Page 49
(Review dace 1 January 1986)
TABLE 12
JAPANESE PVC PRODUCERS - START-UP DATES va ASL CASES
START-UP TEAR 1950
T5TI 1952 1951
1955 1956 1957 1960 1964 1966 1$6> 1968 19^0
1971 1973 1974
COMPANY NAME
Chisso Corp Ranegafuchi Rag Tekkoeha Mitsui Toatau Mitsubishi Mon Sumitomo Rag Denkl Kagaku Nippon Zeon Toa Gosei Rvo-Nichi Nippon Zeon Nisshln Kagaku Kureha Rasel Shlnatsu Rag Denki Kagaku Ranegafuchi Rag Chisso Corp Tokuvama Seksul San Arrow Ragak Sumitomo Rag Ryo-Niehi Shlnecsu Rag Chisso Corp Denkl Kagaku Ranegafuchi Rag Kawasaki Yukl Mitsui Toatsu Nissan Kagaku Shlnetsu Rag Tekkosha Asahi Glass Toyo Soda
1975 1977
Cantral Kagaku Tovo Soda Unknown
LOCATION
Minamata Osaka Sakata Nagovs Tokkalchl Kikumoto Shibukawa Rambara Tckushima Uozu Takoaka Takeo Nishiki Naoetsu Ohmi Takasaco Chiba Tokuvama Tokuyama Chiba Mlzushlma Tokuvama Mlzushlma Gol (Chiba) Kashina Kawasaki Sakai Chiba Kashina Tokkalchl Hayatsukl Sakata Yokkalshl Kawasaki Tokkalchl Kashina
ASL CASE NUMBER
TEAR OF 1st EXPOSURE
01. 02
33. srf
URL 13825
WFX/ASL 2 - LANGIOCASES,54
Page 50
(Review date 1 January 1986)
TABLE 13
SOUTH AND CENTRAL AMERICAN PVC PRODUCERS
START-UP YEAR 1953 1954
l5T5
1956 1960
1961 1965
1966 1967 1968 1970
1971 1975 1976 1977 1978
1 1979
COMPANY NAME
Monsanto Mexlca Policyd Geon Do Brazil Elchlor Electrochlor Vlolastlc Induce (SOC Pacamaoga (1967 start up PET Columbiana Carburo De Col Plastlcos Omega Prime* Policesa Petro Dow Polimeros Mex Rico Chemicals Petroplas Indust Reslstoc Huls Brasil Polychem Policyd PET Camacarl
LOCATION
Lecherla (Mexico) Mexico City (Mexico) Sao Paulo (Brazil) Sao Caetano (Brazil) Capltan Beraudaz(Argentlna) Mendoz (Argentina) Clnco Saltos (Argentina) Paramonga (Peru)
) Cartagena (Colombia) Medellin (Colombia) Mexico Puebla (Mexico1)
Managua (Nicaragua) Conception (Chile) St Martin Puebla (Mexico) Guvanllla (Puerto Rico) EL Tablazo (Venezuela) Tlazcaie (Mexico) Cubato (Brazil) El Salvador Coatzacoalcos (Mexico) Camacarl Bahia (Brazil)
ASL CASE NUMBER
YEAR OF 1st EXPOSURE
.
URL 13826
WPX/ASL 2 - LANGIOCASES.55
i
Page 51
(Review dace 1 January 1986)
TABLE 14 AUSTRALASIAS PVC PRODUCERS
START-UP TEAR
COMPANY NAME
Mid 1950 ICI AuaCralla
1960a B F Goodrich
Lace 1970a ICI Auatralla
LOCATION
Botany, Sydney Melbourne Laverton Melbourne
ASL CASE NUMBER
YEAR OF lat EXPOSURE
URL J3827
WPX/ASL 2 - LANGIOCASES.56