Document R3X3jDenD7zx7kjXo68Bg3dn
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UNITED STATES ENVIRONMENTAL PROTECTION AGENCY
BEFORE THE ADMINISTRATOR
In re:
Proposed Toxic Pollutant Effluent Standards for Polychlorinated Biphenyls
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FWPCA (307) Docket No. 4
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AFFIDAVIT OF ROSCOE M. MOORE, JR.
Roscoe M. Moore, Jr., being duly sworn, deposes and, says:
1. I am currently employed as an epidemiologist by the
National Institute for Occupational Safety and Health (NIOSH),
at 5600 Fishers Lane, Rockville, Maryland. My biography is
attached to this affidavit as exhibit 1.
2. As part of my duties at NIOSH I was'involved in the
preparation of a "Dear Colleague" letter" which was sent out on
August 20, 1976, by Dr. John F. Finklea, Director of NIOSH. A
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copy of that letter is attached to this affidavit as exhibit 2.
3. In this letter NIOSH reviewed the preliminary results
of an epidemiologic analysis based on medical records of Mobil
Oil Company employees exposed to PCBs at Mobil's Paulsboro,
New Jersey plant.
4. Among the 92 workers studied, for whom adequate medical
records were available, eight cancers (in seven workers) were
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observed between 1957 and 1975. Of these eight cancers, three were malignant melanomas and two were cancers of the pancreas. This is significantly more skin cancer (melanoma) and pancreatic cancer than would be expected in a population of this size (based on the Third National Cancer Survey).
5. Based on these findings and those reported earlier on the carcinogenicity of PCBs in test animals, it is my conclu sion that when the results of further studies on occupationallyexposed individuals are completed, there is strong'likelihood that PCBs will be shown to be carcinogenic to humans.
*/ 6. NIOSH is currently conducting such follow-up studies
on workers occupationally exposed to PCBs.
Sworn to and subscribed before me
this
November, 1976.
Notary Public My commission expires:
STLCOPCB4069824
' - 1 ' 1)R. RQSCOE MICHAEL MOORE, JR.
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ADDRESS:
14315 Arctic Avenue Rockville, Maryland 20853
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TELEPHONE: 301-871-8578 (Home) 301-443-3843 (Office)
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BORN: December 2, 1944 -- Richmond, Virginia
FAMILY: Wife: Patricia Haywood, B.S. in Nursing, Tuskcgee Institute, 19G6; C.R.N.A., School of Anesthesia, University of Michigan, 1969.
Son: Roscoe Michael Moore, III, born May 16, 1971 Son: John Haywood Moore, born April 6, 1973
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EDUCATION
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Tuskegee Institute, Tuskegee, Alabama, 1962-1965, B.S. - 1968
` Tuskegee Institute,- Tuskegee, Alabama, 1965-1969, D.V.M.
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Chairman of the Honor Code, School of Veterinary Medicine, 1967-1968
President of Student Chapter of the American Veterinary Medical Association, Tuskegee Institute, 1968-1969
Congressman to the Student Government Association,'Tuskegee
Institute, 196S-1969
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Who's Who in American Colleges and Universities, 1968-1969
University of Michigan, Ann Arbor, 1969-1970, M.P.H. in Epidemiology -
University of Maryland, College Park, February 1971 - May 1971, evening
course in Spanish
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CONTINUING EDUCATION PROGRAMS
Fortran Training Course at the Center for Disease Control, November 8-12, 1971
Pe sticidcs and Public Health Training Course, sponsored by the Environmental Protection Agency (EPA), February 1-4, 1972, AtlanLa, Georgia
Advanced Course - Pesticides and Public Health, sponsored by EFA,
May 16-19, 1972, Atlanta, Georgia
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CONTINUING EDUCATIONS PROGRAMS (COH'T.)
(Jrid Management Course,sponsored by Scientific Methods, Inc., October 21-26, 1973, Morristown, New Jersey
Neurology Course, sponsored by D.C. Academy of Veterinary Medicine, April 4-5, 1974, Fairfax, Virginia , *
Pharmacology Course, sponsored by the Food and Drug Administration, May-June, 1974, Rockville, Maryland
Immunology Course, presented by Johns Hopkins University, October 25 - December 11, 1974, Rockville, Maryland
Comparative Pathology Course, sponsored by the Department of Defense, Armed Forces Institute of Pathology, May 10-12, 1976, Washington, D.C.
WORK EXPERIENCE
January 1976 - Present
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A Veterinary Medical Officer in the U.S. Public Health Servioe, stationed at the- National Institute for. Occupational Safety and Health (NIOSH), Rockville, Maryland.
Chief, Technical Evaluation and Review Branch, Office of Extramural . Coordination and Special Projects (OECSP), NIOSH, with primary
responsibility in conducting and coordinating short-term technical studies including evaluation of toxicologic information transmitted to the Institute for review. Also, maintaining and supervising . the NIOSH Current Intelligence System. This system prepared back ground information on potentially hazardous substances in the occupational environment including toxicity to man and animals, production and uses, and the potential population at risk. This system informs the occupational health community, other government ' agencies, management, labor and public interest groups of new information on potential occupational health hazards.
In addition, as Epidemiologist'for the Office of Extramural Cooi'dination and Special Projects, provides the necessary sta tistical and epidemiological information to quantitate the relative risk.of human exposure to chemical substances in the work environment.
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'WORK EXPERIENCE (CON * T.)
December 197A - January 1976
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A Veterinary Medical Officer in the U.S. Public Health Service, stationed at the National Institute for Occupational- Safety and Health (NIOSH), Rockville, Maryland. .
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Chief, Priorities Evaluation Branch, Office of Occupational Health Surveillance and Biometrics (OOHSB), NIOSH, with primary responsi bility in directing the development, implementation, and maintenance of the Priorities Evaluation System which provides guidance to the Institute Director and the NIOSH scientific staff for the allocation of resources to assure maximum effort in combating health hazards in the work environment.
In addition, as Senior Medical Epidemiologist for the OOHSB, provide the necessary statistical and epidemiological information to quan titate the relative risk of human exposure to chemical substances ' in the work environment.
July 1973 - December 1974
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A Veterinary Medical Officer in the U.S. Public Health Service,
stationed at the Food and Drug Administration (FDA), Rockville,
Maryland.
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A Surveillance Officer, Bureau of Veterinary Medicine, Food and
Drug Administration with major responsibility in evaluating the
safety, reliability, and efficacy of veterinary drugs for the
target species as well as human safety with respect to tissue
residues in food animals. Also, have been active in drug residue
monitoring in edible tissue while serving as FDA consultant to
the States of Wisconsin and New York. In addition, a member of
' the Project Advisory Group on FDA contracts for Heavy Metals
Research. Primarily functioning as a toxicologic epidemiologist
for the Bureau. ^
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July 1971 - June 1973
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A Veterinary Medical Officer in the U.S. Public Health Service,
stationed at the Center for Disease Control (GDC), Atlanta,
Georgia.
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An Epidemiologist with the Epidemic Intelligence Service (EIS) with primary responsibility for national psittacosis, listeriosis, viral pox, Venezuelan equine encephalitis, and animal bite sur veillance. A consultant to Family Planning Activities at CDC to develop animal models for reproduction and population studies. Also, CDG Liaison, Rabies Control Program, Dade County, Florida. In.addition, consultant to the Alabama and Florida State Health Departments on Lead Toxicoses.
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WORK EXPERIENCE (CON'T.)
September 1970 - June 1971
Senior Assistant Veterinary Officer in the U.S. Public Health
Service, stationed at the National Institutes of Health (Mill),
Bethesda, Maryland. .
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A member of the Animal Disease Investigation Service with major responsibility for prevention and control of diseases within the germ-free and specific pathogen-free animal colonies at NIH. In addition, assisting NIH Investigators with research problems related to animal disease.
Summer 1968
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Worked as a Veterinary Trainee with the U.S. Department of Agriculture, Animal Health Division in the State of Georgia.
Summers of 1965 and 1967
A tutor in the Tuskegee Institute summer education program, a
poverty program operating in the "Black Belt" counties of Alabama.
Taught biology in special science centers to high school aged
children in this program.
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While in School at Tuskegee
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I financed my education through Work Study7 Program, Federal loans, and scholarships.
PERSONAL
Professional Affiliations
Member:
American Public Health Association
Action Board Member (1974-1976)
Joint Policy7 Committee Member (1975)
American Association of Food Hygiene Veterinarians
American Association for Labor'atory Animal Science
American Society of Laboratory7 Animal Practitioners
American Veterinary Medical Association
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Conference of Public Health Veterinarians
Drug Information Association
Society7 for Epidemiologic Research
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Professional Affiliations (con't.) .
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Member by Election:
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American College of Veterinary Toxicologists (Associate Fellow)
Society for Occupational and Environmental Health
Veterinary Cancer Society
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Appointments:
An Advisory Committee member on curriculum for the School of Agriculture and Natural Resources, Washington Technical Institute, Washington, D.C. (1974 - Present)
External Reviewer for the National Cancer Institute's Bioassay Program (Trichloroethylene, Chloroform) (1975 - Present)
NIOSH Occupational Carcinogenesis Task Force - Working Group on Mutagenicity Testing (1975 - Present)
Awards
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United States Public Health Service (USPHS) Commendation Medal Award, April 2, 1976, for outstanding performance in the develop ment of a Current Intelligence System for the National Institute for Occupational Safety and Health, and dedicated service to the occupational health mission of the organization.
Licensure
Licensed to practice Veterinary Medicine in Alabama, fGeorgia, and
Virginia.
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Non-Professional Affiliations
Alternate delegate representing the Division of Research Services (DRS) at NIH in the Recreation and Welfare Association (1970-1971) '
A member of the Director's Advisory Committee of DRS. This com mittee is concerned wittr equal employment opportunities with DRS at NIH (1970-1971)
A member of the National Wildlife Federation (1970 - Present)
An Associate Member of the Intcrreligious Foundation for Community
Organizations, Inc. (1974 - Present)
An Associate Member of the American Committee on Africa (1974 - Present)
Hobbies
A philatelist and tennis enthusiast
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PUBLICATIONS
Moore, R. M., Zehmer, R. B.' Listeriosis in the United States. 1971. J. Infect. Dis., Vol. 127:610-611, 1973.
Moore, R. M. Human Orf in the United States. 1972.
Dis., Vol. 127:731-732, 1973. . _
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J. Infect.
Moore, R. M., Zchmer, R. B., Moulthrop, J. I., Parker, R. L. Surveillance of Animal Bite Cases in the United States. 1971-72. Arch. Environ. Hlth. (In Press)
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.Moulthrop, J. I., Moore, R.' M., Parker, R. L. Venezuelan Equine Encephalitis Surveillance in the United States. 1972. J. Infect. Dis., Vol. 127:572-573, October 1973.
Durfee, P. T., Moore, R. M. Human Psittacosis in the United States. 1971-1973. J. Infect. Dis., Vol. 131:193-194, 1975.
Lloyd, J. V., Decoufle, P., Moore, R. M. Background Information on Chloroprene. J. Occu. Med., Vol. 17:263-265, 1975.
Lloyd, J. W., Moore, R. M. , Breslin, P. P. Background Information on Trichloroethylene. J. Occu. Med., Vol. 17:603-605, 1975'.
Kaufwann, A. F., Moulthrop, J. I., Moore, R. M. A perspective of Simian Tuberculosis in the United States. 1972. J. Med. Primatology, Vol. 4:278-286, 1975.
Lloyd, J. W. , Moore, P.. M., Woolf, B. S., Stein, H. P. Poly chlorinated Biphenyls. J. Occu. Med., Vol..18:109-113, 1976.
. Levine, R. J., Moore, R. M., McLaren, G.j Barthel, V7. F. ,
Landrigan, P. J. Occupational Poisoning, Animal Deaths, and
. Environmental Contamination at a Lead Scrap Smelter. June
Issue, AJPH, 1976.
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Moore, R. M., Moulthrop, J. I., Sather, G., Holmes, C. L., Parker, R. L. Venezuelan Equine Encephalitis Vaccination Survey in Arizona and New Mexico. 1972. Public Health Reports (Submitted).
Moore, R. M. The Epidemiology of Animal Bite Cases in the United
States. Proceedings of the 11th (1976) Annual Veterinary
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Symposium, School of Veterinary Medicine, Tuskegee Institute
(In Press).
PUBLICATION EXPERIENCE
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. Prepared monthly surveillance reports for the Center for Disease Control concerning listeriosis, psittacosis, and Venezuelan equine encephalitis from 1971 to 1973.
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kUDLIC SPEAKING
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Chaired session at the 102nd Annual Meeting of the APIIA in New Orleans on October 22, 1974, entitled "Zoonoses and the Non-White and Poor."
. "Public Health and Legal Significance of Drug Residues in Food Animals" presented at the Ninth Annual Symposium, School of Veterinary Medicine, Tuskegee Institute, Alabama, April 9, 1974.
"Environmental Lead Contamination - Effect of Humans, Animals, Soil and Plants" presented at the Annual Epidemic Intelligence Service (EIS) Conference at the Center for Disease Control (CDC) in Atlanta, Georgia on April 9, 1973.
"Equine VEE Vaccination Survey, 1972" presented at the Annual EIS Conference at CDC in Atlanta, Georgia, April 13, 1973.
"The Epidemiology of Animal Bite Cases in the United States" ' presented at the Eleventh Annual Symposium, School of Veterinary
Medicine, Tuskegee Institute, Alabama, April 12, 1976.
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DEPARTMENT OF HEALTH. EDUCATION, AND WELFARE
PUBLIC HEALTH SERVICE CENTER FOR DISEASE CONTROL
August 20, 1976
NATIONAL INSTITUTE FOR OCCUPATIONAL SAFETY AND HEALTH 5600 FISHERS LANE
ROCKVILLE. MARYLAND 20852
Dear Colleague:
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In a June 24, 1976 letter, Mobil Oil Corporation advised the National Institute for Occupational Safety and Health (NIOSH) of a possible association between occupational exposure to polychlorinaXg-d-'biphenyls (PCBs^ and cancer in humans. Mobil Oil reported preliminary results of an epidemiologic analysis based on medical records of employees exposed to PCBs at their Paulsboro, New Jersey plant. This study was conducted by Professor Anita K. Bahn (School of Medicine, University of Pennsylvania) and is being reported by Dr. Bahn in a letter to the .editor of the New England Journal of Medicine, August 19, 1976.
The study included two cohorts of Mobil employees who were reported to have had varying exposure to Aroclor 1254 (a mixture of PCBs). The ' .cohort of research and development employees was exposed to PCBs be tween 1949 and 1957 and the cohort of refinery plant employees between 1953 and 1958. The extent of exposure of these workers to other chem icals is not known. The cancer incidence among these workers for the period 1957 through 1975 was determined using Mobil medical records. . Because medical records for 37 employees were incomplete, these workers ` were excluded from this analysis.
Among the 92 workers in these two cohorts for whom adequate medical records were available, eight cancers (in seven workers) were observed between 1957 and 1975. Of these eight cancers, three were malignant melanoma and two were cancer of the pancreas'. ([This is significantly more skin cancer (melanoma) and pancreatic cancer than would be ex pected in a population of this size (based on the Third National Cancer Survey) The remaining cancers were found at three other sites ' in two employees; sarcoma of the right thigh and multiple myeloma in one employee, and recto-sigmoid cancer in the other.
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Page 2 - Dear Colleague
NIOSH is unaware of any other published animal or humandata which sug gest a correlation between exposure to PCBs and skin (melanoma) or . panCVeaTic~cancer.~~ However7'hepatomas (mice, Aroclor 1254) and hepatoceixular carcinomas (mice, Kanechlor 50*0; rats, Aroclor 1260) have been reported in PCB feeding studies of laboratory animals.
Background information on PCBs has been summarized in the NIOSH Current
Intelligence Bulletin on Polychlorinated Biphenyls issued to the occupa
tional health community on November 3, 1975, and subsequently published
in the Journal of Occupational Medicine, Volume 18, pages 109-113,
February 1976. Since the NIOSH Bulletin was first issued, a number of
large firms have introduced products (e.g., butylated monochlorodiphenyl
oxide and dimethyl siloxane polymer) claimed to be fire resistant
dielectrics which can serve as alternatives to PCBs. In addition, one
of the large domestic transformer manufacturers announced that it will
cease using PCBs as fire resistant transformer fluids at the end of
this year. NIOSH would like to stress that alternatives for PCBs should
be thoroughly studied to assess the consequences'they may pose to human
health.
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To aid in evaluating PCBs as a potential occupational health problem,
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NIOSH would welcome receiving reports of studies regarding the possible
association between exposure to PCBs and human cancer.
Your cooperation in this matter is appreciated.
Sincerely yours,
'John F. Finklea, M.D. Director
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REPORT ON PAULSBORO,`N.J. . MOBIL OIL PLANT STUDY
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Department o f Community Medicine
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University of Pennsylvania
School of Medicine
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(Epidemiology)*
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Assisted by I. Rosenwaike, M.A.'; N. Hermann, Ph.D. ;
3'. Grover, Ph.D. ; J. Stellman, Ph.D., University of
P< ennsylvania - Fox Chase Cancer Ce nter.
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OUTLINE OF REPORT
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INTRODUCTION
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Resume of Literature
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METHODOLOGY
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I. Data for the Research and Development Employees.
' II. Data for the Refinery Employees
FINDINGS
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DISCUSSION OF FINDINGS AND. LIMITATIONS OF T1IE D/VIA
' RECOMMENDATIONS
i' TABLES
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APPENDIX: LITERATURE REVIEW
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. * INTRODUCTION
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`In the Fall of 1975, the Medical Director and the management
at Mobil Oil became aware of possible health hazards due to'exposure
to polychlorinated biphenyls (PCBs) among two small groups of employees
at their Paulsboro, New Jersey plant. Although PCB has not been
in use for some time, the possibility exists that late effects such
as cancer or liver disease could result from such exposure. The
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latter has been noted in experimental animals.
A thorough examination of available medical records was promptly
made by Dr. J. Rodney Meredith, Medical Director of the plant. These
^ records were supplemented with other sources of information with
regard to exposure to PCB.
. The report that follows is a preliminary -epidemiologic analysis
of the data furnished to us by Dr. Meredith. Suggestions, for further
'i t ' epidemiological studies are also included in this report.
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Resume of Literature
^ ^tailed literature review has been included as an appendix.
1\ s4mmary is presented here, polyc^^ j nated biphenyls (PCBs) describe a group of synthetic
Cf,lnrlnatc.d organic compounds, which have been manufactured in the
c*nc^' 1929 and have been widely used in industry. Commercial
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VCJW are 9 enerally mixtures of many different chlorinated biphenyls.
?254, a trademark of the Monsanto Co., is a mixture of
CfJ/Inf*na^eQ biphenyls and contains 54% chlorine.
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PCBs &re nQt easily metabolized and tend to accumulate in
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tis sue. Polychlorinated biphenyls were found in measurable
fjfti/iiihts irj
1% of- 637 samples of human adipose tissue collected
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General population in 38 13. S. cities.
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^ h*s been reported that workers engaged in the manufacture
0f /jfochlc-j. were affected with acne-like condition on the face
tttid neck arjjj -that fumes may penetrate the clothes and cause acne-like
Inris
develop on the covered parts of the body.
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In aij outbreak of poisoning in Japan due to ingestion of rice
bj fill
^nich had been contaminated by PCB (Kanechlor 400) common
uyiiijil.oms deluded: pigmentation of the skin, acne-form eruptions `
ir.vi follicu2ar accentuation, increased eye discharge and swelling of
cye^ids, <ind feeling of weakness. 7\ dose-response relation
** ^"crv6d. Children born to mothers who had eaten the contaminated
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'ft Wf r a rc smaller than averaqe and had discolored skin, although
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c ^ldren grew older the stained skin gradually faded.
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Hats fed hrochlor showed more liver abnormalities including
hepatocellular carcinomas than did control rats. No unusual features
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were noted in tumors of other organs, and there were no apparent
differences in incidence in tumors between experimental and control
animals.
- The results of applying.a mixture of isomers of chlorinated .
biphenyls to the skin of guinea pigs, rats and rabbits were: (1)
changes of the liver among guinea pigs (2) liver and skin changes
among rats and rabbits.
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Reproductive failure has been noted in monkeys exposed to PCB. '
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` METHODOLOGY
X. Data for the Research and Development Employees
A. Study group and exposure
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Sixty-four Research and Development employees are reported to
have been exposed to Arochlor 1254 in the interval between 1949 and
1957, Of Che 64 men, 35 are still employed by Mobil;. 29, including
3 deceased employees, are no longer employed (Table A), For 16
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of the 29 not currently employed, medical information is missing
on an average for only the last two to three years
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therefore, these men are included in the analysis.
(Table B);
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For the remaining'
13 men there is no Mobil medical record or follow-up information for the
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past 12 years or more; therefore, these 13 are excluded from
this analysis.
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. Based on exposure data estimated by an employee. Bob Wilson, the .
51 men included in the analysis were divided into two groups: (a) exposed
to contact with forming oil, and (b) other ("probable", "unlikely",
"unknown") exposure. Another observer, Ed Rosinski, developed a
scale attempting to quantitate exposure. A summary of the total
group (64) and the observed group (51) cross-classified on the two
ratings (Wilson and Rosinski) is shown in Table C. It should be
noted that the 13 persons excluded from the analysis are about evenly
divided between the (a) and (b) exposure groups (7 and 6 respectively) .
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B* Observation period
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ft 6 D employees were exposed to PCB f.ox various times during
the years 1949-1957. The exact dates of exposure were not indicated
in the material we used. For this analysis, therefore, observation
time was assumed to be December 31, 1957 through December 31, 1975.
This procedure understates the. observation period (if the average
beginning point is assumed to be midway between 1949 and 1957, i.e.,
1953) but at the same time allows for an average minimum cancer
/ induction period of about four years.
. Information on age was'available for all 51 employees. / Person year's of observation by age category were constructed for the'51
employees for the 18-year interval between 1957 and 1975. (It was i.
assumed that age reported for current employees is as of 12/31/75),,
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.,.idnumber of new cancers c. ErfJJ;---------------;------------------------------------------
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.ji^ptcd incidence of cancer among the group under study E^*/
. I he ceriod 1957-1975 was based on the Third National during "' .
inr\v incidence Data (NCI Monograph 41, March 1975) which
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, . Incidence rates by sex, race, and five year age groups reportr- '
- , ,,#,11-3 971. Our expected values were based on rates for male:
for 19"' ,;^s) , by age, but are rough, for the following reasons
(all rr--*7 *
0j Incidence rates for males have tended to increase over
, I he levels in 1969-71 may be slightly higher than that
tame s''
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^jrpected rates would tend to reduce any difference between higher
.1 and expected cancers.
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On the'other hand, age-specific cancer mortality in New
/as measured for the period 1950-69) was considerably Jersey*
i han the national average; hence the expected levels in this
higher
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uPW population probably should be higher than the national j New JO.?1* 7 *
.. Ipv,-', The use of U.S. rates, rather than New Jersey rates
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nd to -ncrease any difference between observed and expected,
vould f,,n
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Jersey rates arc believed to be a reflection of .
i j,,'r//J dilating expected incidence of cancer the rates used were **''%<> laf the '`total" (white and black) population because (D the *-. .ju distribution of the study population was not immediately r<i o **x * '1` '>](!, hn informed guess is that 0-1 of the 64 Research and
\*-uncut cm.-loyecs and 2-3 of the 65 refinery employees .wore
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occupational-environmental factors and therefore the Nov/ Jersey
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population is a less desirable control group than the total U.S.
population.
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The expected cancer rates were applied separately to exposure classes (a) and (b) yielding the expected numbers of cancers shown in Table E.
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II. Data for Tho Refinery Plant: Employees .
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h. Study group and exposure
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Sixty-five employees at the Bead Plant in Paulsboro are reported
as exposed to Arochlor 1254 for varying lengths of time during the
interval between October 1953 and June 1958.. V7ith the exception
of one individual listed as exposed for one month, all' exposures
were from 6 to 56 months.
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Of these 65 "exposed" men, 30 are still Mobil employees and
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35, including 3 deceased, have terminated employment (Table A).' Of
these- 35, 11 had current medical records yielding a total of 41
men (30 plus 11) for the study population (Table D). For 12 men
.(all terminated by 1960) no charts were available and for another
12 men charts are available only until the date of termination in
1961 or 19.62, Therefore these 24 men have been excluded from
the analysis.
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It should be noted that no record was provided on extent of -
. sxposure of Refinery Plant employees but only months of exposure,
therefore no classification of this group was made in the analysis.
1. Observation period
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Observation time was calculated from the end of 1957 thru the
nd of 1975 for the 41 men included in the analysis.
* Expected number of new cancers
, Person-years of observation and expected cancers were *
alculated .as for the R and D employees (see Table E).
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# . FINDINGS
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The following is a resume of the preliminary analysis of this
.
data (Table E):
'-
;
I
X. .Eight cancers'were observed in the total population versus 5.7
*
expected. This difference is not statisticcillv significant.
' However, of the 8 cancers, 5 (62.5%) were either melanoma (3)
. or cancer of the pancreas (2). This .compares with an expected
percentage of about 5 percent of all cancers in the general
*..
population.
*
`
''
*i .
-
-
2. One melanoma occurred among the refinery employees. The
remaining tv;o melanomas and the two cancers of the pancreas
occurred only among the 31 (60%) of the R & D employees who were
listed as exposed to contact with Arochlor 1254. The percentages
that these cancers are to all cancers found, as compared with
expected percentages based on the general population,are highly
' significant (Table F) .
.
-.
3. Looking at the data for all study employees on a rate basis '
-
.
or risk of developing cancer (the preferred type of analysis),
r
3 melanomas were observed versus only 0.1 expected, and 2 cancers
'
of the pancreas observed versus only 0.2 expected (Table E).
.
For the R & D employees classified as "yes" to exposure to
Arochlor 1254, the respective P values arc highly significant
' (Table <F)'.
' *
. '.
.
"%
DSW 307434
- ;
STLCOPCB4069844
",,'
-
. .
Other f jridings:
'
.
-
^
*
.
'i
For the three cases of melanoma of skin the site
location and age at diagnosis were as follows: right upper arm
(57 years), upper lumbar region (51 years) and left anterior chest
(42 years). Time from the data of first exposure to Arochlor 1254
\
\
to time of dicignosis for the three cases were: 10-14 years (calculated,
exact duration not given in memo), 17 years, and 10 years, respectively.
The two employees who developed cancer of the pancreas were ages
.57 and 62 at the time of diagnosis. The times since first .exposure
a were 13 years and 24 years. Both employees were non-smokers.
. Carcinoma was also found in three other sites, among two R G D
employees. Cancer of recto-sigmoid was diagnosed in a group (b)
4
. 56 year old employee approximately 21 years after exposure. Another
employee in group (a) developed sarcoma of the right thigh at age 42
(14 years after exposure); ten years later he also developed multiple
myeloma.
:.
-
i i i
4
DSW 307435
STLCOPCB4069845
DISCUSSION AND LIMITATIONS OF THE DATA
These findings, although preliminarv and excluding data
On over one-third of the refinery workers and one-fifth of
the R It D workers, suggest a probable causal relationship between
exposure to Arochlor 1254 and melanoma. Even if all of the untraced
pen in the "Yes" exposure group were found to have not had melanoma
the P value would be virtually unchanged (P= .0015 instead of .0010).
These findings are also coherent with biology (i.e. biological)
Plausibility) . Chloracne is .known to be a freauent acute dermatitis '
occurring upon exposure to volatile chlorinated hydrocarbons (See
literature review'.} In the Japanese women who ingested contaminated
rice oil, both the women and their offpsring developed skin pigmenta
tion. Histological examination of a stillborn fetus shewed a "marked
hyperkeratosis... a marked increase of melanin pigments in the
.
basal cells of epidermis" (6). It should be pointed' out also that
melanoma on unexposed portions of the body are relatively rare. .
. As in the Japanese study, a dose-response gradient may be postulated
as evidence of a causal relationship.. Although unverified, it is
believed that the R & D group had a much higher exposure to Arochlor
1254 than did the refinery group. This is consistent with the larger
number of cancers among the R & D men.
'
The association of Arochlor 1254 with cancer of the pancreas is also statistically significant but weaker than that with melanoma.
Furthermore, the possibility of cancer of the pancreas being asso
5? CO Q
ciated with other chemical exposures in U f. D employees must be
Considered. Li and Frnumeni in "Cancer .Mortality Among Chemists"
(journal of the National Cancer Institute, November 19G9) reported an excess of deaths from cancers of the pancreas and lymphatic
30743q
STLCOPCB4069846
I
' hro.chlor 1254 is no longer being uccd at Mobil but J?CJ3s arc
,
being- manufactured by Monsanto, are used in a number of .
Industrial operations and have been dumped as a waste product into
cater supplies.
_
-
' If, as seems likely,PCB is a causative agent of melanoma, this
cnowledge must be acted upon promptly. In terms of surveillance
tor melanoma it should be noted that early diagnosis of this malignancy
1
greatly affects survival:
Stage of Disease at Diagnosis
localised regional
Relative
. Survival (%) *
5 yrs.
10 yrs.
73 67
33 32
Our data on a small cohort shows a very hiah relative risk of
i
3eve3oping melanoma upon exposure to this PCB. 'This study should be
replicated in other industrial settings where other persons have been
jxposed to PCBs. The Japanese exposed to this agent in 1968 developed
ikin pigmentation (as did their offspring) and chloracne. Probably
n insufficient time has elapsed for cancer to develop in the Japanese
i
i
f
t
r
v
cohorts but surveillance for melcinoma is essential. t
'
^ Survival from cancer of the oancreas is less likely to be affected i *
>y early detection. . nevertheless, persons at high risk should be
.
identified:
. .
.
Stage of Disease at diagnosis
'
Localised Regional
Relative
Survival U) *
3 vrs.
5 vrs.
7A
22
J
DSW 307437
-i
Source: Knd Bcsults in Cancer, Hooort >10. <1 , NIII, 197?.. These are dative .survival rateswhich ad-just for "nornal" mortal! ty with ospoet to ago and oeriod of observation.
| I
STLCOPCB4069847
13
7\o stated, exposure to other chemicals may be implicated in
cancer of 'the pancreas in particular.
''
'_
*.
Possibly other cancers may also be associated v/ith PCD.
.
Subseauent
medical history of Paulsboro retired employees would be.important
in this regard, also. Data for a larger employee population probably
would be necessary for assessing the risk of other cancers, however.
'
The major limitations of the data in our analysis should be
mentioned:
'
t
1. Data on duration,' age, and extent of exposure are limited.
Also,
. .
no information is available on other chemical exposures.
2. No information is available on the occurrence of cancer in 37,
.
1 or one fourth of all the employees in both groups. One or two
missed diagnosed cancer cases of melanoma, pancreas, or other site
could markedly affect conclusions.
.
3. The number of observed cancers among men included in the analysis
may v/ell be understated because there is no. reDorted follow-up (other
than death) for those study employees who were terminated. This
; includes for R & D employees three living employees terminated five
!
"'
.
! to ten years ago and one 11 years ago. All are presently 69 years
,'
Of age or older and therefore are in a high risk group for cancer
in general. Similarly among the refinery employees information is
; leicking on several years of follow-up of recently retired employees.
In effect, the methodology employed for all of these employees assumes
i that no cancers developed amono them during- this period.
' ,
'
-.
: '*
.
, `
. .
`
*
' *
' DSW 307438
< l j
--- . / .
\
i
*( t
>1
STLCOPCB4069848
/ 4,
'4va*Y,,i>jA.U' 4--.;'. .V'
t
14
..
' ' * * I
i
.i
* * *
Another rna-jor limitation is the relatively-short observation
.
period. Induction of cancer due to small doses of this agent may
require more than 20 years to manifest itself. Current information
indicates that for environmentally induced cancers in adults, in
general, the average latency period between first exposure and disease
jls in the range of 10-30 years.
j
, Our methodology (observation period beginning in 1358)- under
states the risk of cancer if there is a long latent period. For
/
example, if the minimum latent'period is ten years the entry period
for the individual workers into the study cohort should begin at i
varying times between 1959 and 1967 (or 1968) rather than in 1958.
\ J
STLCOPCB4069849
;COMMnNPATIO:iS
15
*.
.`
i . 'i
, Vie urgently recommend that steps be taken immediately to insure
." *
<
rompt arid periodic screening examinations for melanoma among all
arrant!y employed and terminated employees (both R & D and refinery)
ar whom there has been any possible exposure to PCD; i.e./all survi-
ors of Vhe potential total of 129 men exposed. We also urge prompt
Dvelopment and distribution of appropriate informational material
or these employees. These recommendations are based upon (1) the
/ata made available to us and our analyses (under the assumptions of
ur statistical models) which show a highly significant statistical
ssociation between "exposure" tor Arochlor 1254 and subsequent inci-
!ence of melanoma (2) the biologically plausible relationship between i arochlor 1254 and melanoma in view of the freouency of reported chloracne
lermatitis upon exposure to this agent and the Japanese study. Some
.vidence for a dose-response relationship is also present.
!. From' an epidemiologic standpoint it is also of high priority to
!ollow-up the 37 men (former R & D and refinery employees) for whom
:urrent records are not available to determine if they have had any
:ancers, whether or not currently alive. The follow-up could be in
:hc form of a general health questionnaire by mail, telephone, of
.
>crsonal interview. . Similar information should be obtained for 23
termincited employees who were included in the study but whose medical
status for the last several years is unknown.
.
1. The above recommendation addresses the oroblem of "missed cancers".
In addition the epidemiologic studv needs.sharpening up with respect
to exposure data (who were exposed; date's and. intensity of exposure-
**
/
^
*;omc of this information is already avoidable in Dr. Meredith's records)
<<
DSW 307440
i j i i j i
l
Itt i
STLCOPCB4069850
1C I
t
.'
,
.
*
i.
-
**
so that the .appropriate classification of the employees by these
parameters can be made'. Also, this information will assist in better
n uantification of the dose-response relationship.
?herefore, we need to conduct a thorough epidemiologic study by obtaining
xposure and other data via a questionnaire administered to all of
;he 64* R & D employees and 65 refinery employees (or the next of (
k
iin, if dead) . Such auery would include also history of cancer
-
5f any site (including squamous or basal cell carcinoma which might
#,
hot be known to medical records), chloracne dermatitis, liver disease,
.
md other significant medical conditions reauiring hospitalization;
smoking history; family history of cancer;fair skin color; exposure
to other chemicals.
*
i'
.
'
- rFor.this epidemiological study, in addition to the use of
'
.
; I
"internal" controls (the subgroup with minimal or. zero exposure) , it
yould be desirable to have another control group such as a sample of
\-
`
other R & D or refinery workers and/or of other types of workers.
'
t
t
`
This i.
real
j
procedure would have the additional `
purpose of the study which if known
advantage of "blinding" might introduce bias in
the
employee responses regarding intensity of PCB exposure.
'
r
5. To`detect other possible cancers which may emerge, conduct in
t .
the near future, and' periodically, health screening examinations of
I `>all exposed survivors (including retirees) for other
|.
other malignancies, and hepatic disease. i.
A modified
skin cancers, CAESCREEN
iquostionnaire' and CAESCREEN examination might,achieve this and other
.
stated objectives. .
'
:.
DSW 307441
,*
Information on exposure-should be obtained not only by the . .
employees reporting for themselves lull, also by requesting them to
`
STLCOPCB4069851
>1
...
17*
i
`
-
.. i
C. If indicated pcrfonn fat biopsies for PCD as one indication of
extent of exposure.
'
7. If possible we would like to also study employees in other plants,
such as Monsanto, where a larger number of emoloyees may have been
exposed to PCD.
.
.
I
8. Study MRDC employees on hydraulic fluid program.
307442 DSNN
ii ii
STLCOPCB4069852
'. #
r o ;
,
#* STABLE a
. ..
**
* -.
.
Ymploycos by present status and by area of work:
Area of Work
R&D Refinery
'Total *
64 '
65
Living At Paulsboro At Other nj ants Terminated
Dead
32 ' 28
3
.
26 .
3(2)
1
2 32 3
2-29
' 60
ROTE* Cancer deaths in parenthesis.
5
58 6
#
OS'N
A43
STLCOPCB4069853
19
Table B
Medical Record Status of 64 Rescrirch f< `Development Employees
* i Medical Bocords Available
.
'
35 Current Employees
'
Died while employed
Terminated at ages 57 to 65 - presumably retirement*
51 Persons included in the analysis
Mo Medical Records
'
13 Terminated or transferred 1362 or earlier: excluded
. from the analysis.
.
64 TOTAL '
...
.
* The-earliest retirement was 1964; the second earliest was 1969.
Half of the retired left in 1973 or later.
.
0S**>7444
1'
STLCOPCB4069854
Table C
'
'
20
'
i
'i
Rating on Exposure to /`.rochlor 12 54 of G4 Research and
Dovclopment Employees
**
Rosinski Rating
.
. .
.. Total
- ,*>
Low to High
64 29
Slight
12
Negligible,question
able
10
No recollection
2
2'ero
11
____Wilson Rati ncr ' (a)
'.
Yes *
38
26
.. 4
.
(b) Other (Probable,Unlikely, Unknown)
26
3
8
/
6 `4
1 .1
1 10
Rating on Exposure.t o Aroc'nlor`1-2 5 4 of 51 Research and Development Employees included in t.'-ns stuev '(Excludes 13 no-rocords available employees)
Rosinski Rating
*
. .
.
'
Wilson Rating
' (a)
.
.'
Total
Yes
-
(b)
Other
.
(Probable, Unlikely,
Unknown)
' bow to High
51 26
Slight
0
Negligible, question
able
9
No recollection
'~
Zero
8
approximate concordance of ratings
OSIN M7445
-<
i!
STLCOPCB4069855
21
Tabic D
..
Medical Record Status of 65 Refinery Employees
30
2
9 ___
41 '
\
Current Medical Records Available
Current Employees
Died either while employed or within a year after
.Terminated in 1967 or later (6 were ages 57 to 64 presumably retirement)-a majority left in 1971 or later.
Included in the analysis
No Current Medical Records
.
1.2 No Medical Records - Terminated between 1955 and 1960.
12 Terminated in 1961-62
*
'
24
Excluded from the analysis
*
'
65 *
TOTAL
iJ {
DSW 307446
STLCOPCB4069856
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STLCOPCB4069857
23
+
` Tabic F
Levels of Stat5stica1 fo cm i flea nee among grouR (a) (Yos) R & D employees
*Pancreas *Melanoma
_________________________P Values.' Observed number versus expected number
As a percentage of all cancers observed compared to expected nercentaces
.0025
. OIG^-
.0010
.007
Assumes (1) that the data fit the Poisson distribution and (2) that there is independence of observations from year to year (this is not necessarily true of Person-year observations).
I
-
I.
*iip '
These P values are not based on tests of prior hypotheses but tests conducted after observation of the data.
-
'
..
'"
.
.
. .
.
.. * .
-
, " . .
*
*
;
i
i (; i. * {* i ^ .
(
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*.
os***448
_. --
i
; i i
STLCOPCB4069858
CERTIFICATE OF .SERVICE
The foregoing Affidavit of Roscoe M. Moore, Jr., was sent by first-class mail, postage prepaid, or hand-doJivcrcd, this 3rd day of November, 1976, to:
Ridgway M. Hall, Jr., Esquire Environmental Protection Agency ' Room 509 - West Tower 401 M Street, S. W. Washington, D. C. 20460
.
Honorable Edward B. Finch Environmental Protection Agency . .401 M Street,. S. W. , Room 1019 Washington, D. C. 20460
.
Ms. Khristine L. Hall Natural Resources Defense 917 15th Street, N. W. Washington, D. C. 20005'
Council,
Inc.
Peter J. Nickles, Esq. Theodore J. Garrett, Esq. Steven S. Rosenthal, Esq. Covington & Burling 888 16tli Street, N. W. Washington, D. C. 20006
Michael K. Glenn, Esq. (American Paper Institute) Dunnington, Bartholow & Miller 161 East 42nd Street New York, New York 10017
^
Philip H. Gitlen, Esq. New1 York State Department of
Environmental Conservation 50 Wolf Road Albany, New York 12233
Roger C. Wills, Jr. Westinghouse Electric Corporation Westinghouse Building Gateway Center Pittsburgh, Pcnnsylvania 15222
' 1
DSW 307449
STLCOPCB4069859