Lorillard
A Comment on 'health Effects of Passive Smoking: Assessment of Lung Cancer in Adults and Respiratory Disorders in Children'. Epa / 600/6-90/006a, 900500
Fields
- Author
- Gori, G.B.
- Type
- REPT, OTHER REPORT
- BIBL, BIBLIOGRAPHY
- FOOT, FOOTNOTE
- SCRT, SCIENTIFIC REPORT
- BIBL, BIBLIOGRAPHY
- Alias
- 87655164/87655194
- Area
- SPEARS,ALEXANDER/EXEC CONF ROOM STORAGE
- Named Organization
- Cdc
- Division of Cancer Causes + Prevention
- Epa, Environmental Protection Agency
- Franklin Inst
- Ftc, Federal Trade Commission
- Hew, Dept of Health Education and Welfare
- Instituto Superiore Di Sanita
- Intl Society of Regulatory Toxicology +
- NCI, Natl Cancer Inst
- Nutrition + Cancer
- Regulatory Affairs Comm
- Society of Toxicology
- Technical Affairs Comm
- TI, Tobacco Inst
- Academy of Toxicological Sciences
- Division of Cancer Causes + Prevention
- Named Person
- Adami, H.O.
- Albanes, D.
- Beaglehole, R.
- Benner
- Brown, C.L.
- Cheng, Y.
- Correa
- Coultas
- Doll, R.
- Dube
- Edlin, C.
- Ekwo, E.E.
- Fisher
- Gao, Y.T.
- Garfinkel
- Goodman, M.T.
- Green
- Grimm
- Hatziandreu, E.J.
- Hiller
- Hinds
- Jackson, R.
- Jain, M.
- Kerigan, A.T.
- Kirk
- Koo
- Kulessa, Che
- Kvale, G.
- Lange, P.
- Lavecchia, C.
- Lebowitz, M.D.
- Leeder, S.R.
- Lees, R.E.
- Lemarchand, L.
- Li, W.X.
- Lowrey
- Lynch
- Mettlin, C.J.
- Miesner
- Mumford, J.L.
- Ooi, W.L.
- Peto, R.
- Pisani
- Pollack, E.S.
- Repace
- Rothman, K.
- Sakurai, R.
- Samet, J.M.
- Stanton, M.F.
- Sterling
- Surgeon General
- Tager, I.B.
- Tenkanen, L.
- Turner
- Varela
- Weber
- Whichelow
- Willett
- Witorsch, P.
- Witorsch, R.J.
- Wu, A.H.
- Wynder, E.
- Ziegler
- Albanes, D.
- Date Loaded
- 05 Jun 1998
- Request
- R1-004
- R1-059
- R1-132
- R1-059
- Master ID
- 87653565/6821
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A COMMENT ON
"HEALTH EFFECTS OF PASSIVE SMOKING:
ASSESSMENT OF LUNG CANCER IN ADULTS
AND RESPIRATORY DISORDERS IN CHILDREN".
EPA/600/6-90/006a, MAY 1990
Dr. G.B.Gori.
The Health Policy Center
Bethesda, Maryland

- 2 -
I have been asked by The Tobacco Institute to review
the draft EPA document entitled "Health Effects of Passive
Smoking; Assessment of Lung Cancer in Adults and Respiratory
Disorders in Children," which was released for public comment
on June 25, 1990. My general conclusion is that this draft
cannot be regarded as a credible scientific document.
CREDENTIALS
I am currently director of the Health Policy Center,
Bethesda, Maryland, a consulting practice with a program of
research in toxicology, epidemiology, risk assessment, and the
formulation of public policy alternatives compatible with
health, safety and the common welfare. For eight years I was
director of the Franklin Institute's Policy Analysis Center,
leading a similar program of basic and applied research for an
independent examination of health hazards and risks, and the
costs and benefits of regulation.
Before joining the Franklin Institute I held
executive positions from 1968 to 1980 at the National Cancer
Institute. From 1972 to 1980 I was Deputy Director of the
Division of Cancer Causes and Prevention, with simultaneous
responsibilities as Acting Associate Director of the
Carcinogenesis Program (1976-78), Director of the Smoking and
Health Program (1968-1980), and Director of the Diet,
Nutrition and Cancer Program (1972-1980). Before 1972 I
served as the Associate Scientific Director of the Division,
which is entrusted with developing an understanding of cancer
causation and of the methods for its prevention. I have been

3
directly active in environmental carcinogensis and health,
nutrition and health, non-ionizing radiation and health, and
the relationship between smoking and health. In recognition,
I received the DHEW Superior Service Award in 1976. Prior to
1968 I held positions of increasing responsibility in
industry, academia, and Istituto Superiore di Sanita, the
national health research center of Italy.
I am a diplomate of the Academy of Toxicological
Sciences, Vice President designate of the International
Society of Regulatory Toxicology and Pharmacology, past member
of the Technical and Regulatory Affairs Committees of the
Society of Toxicology, a member of several scientific
societies and editorial boards, editor of Nutrition and
Cancer, an international Journal, and the author of over 100
scientific publications. A copy of my curriculum vitae is
attached.
INTRODUCTION
Reductionist assumptions have frequently been
employed in the epidemiology of multifactorial diseases.
Although it is recognized that such diseases are influenced by
a multitude of factors, cost considerations often have
dictated the assumption that only one or a small number of
factors are involved. Public health policies based on such
grossly simplistic epidemiologic foundations can easily lead
to unfair treatment for the particular chemical or other
substance that is deemed to be the "culprit" for regulatory
purposes. Yet no impartial jury would convict a defendant who

- 4 -
happened to be present along with many other people at the
scene of the crime, without ascertaining his actual
involvement.
Nevertheless, policy makers often do proceed in this
fashion, offering the justification, as Kenneth Rothman, a
leading epidemiologist, has pointed out, that "the exigencies
of public health problems demand action and that despite
imperfect knowledge causal inferences must be made." (Rothman
1986, p. 17).
Surely there is a need for some bounds to the
uncertainty permitted in the formulation of public health
policy. At the very least it would seem reasonable to require
that all or at least the most obvious competing hypotheses
should be adequately explained away or factored in, before a
suspicion of causality can be linked to a specific factor and
before public policies can be imposed on grounds of reasonable
prudence. On its face this would seem a minimum standard for
fair and sustainable policies.
As a foundation for public policy, the draft EPA ETS
risk assessment does not meet this minimum standard. This
document admits the presence of, but fails to account for, the
multitude of factors that we know must play a part in this
complex epidemiologic scenario. The ETS-attributed relative
risks are very small, and indeed they usually are much lower
than the reported RRs of suspected and likely confounders.
Indeed, it appears that the EPA draft began with a conclusion
and proceeded only with evidence that sustains that

- 5 -
conclusion: the use of one-tailed probabilities, the dogmatic
exclusion of thresholds, the selective exclusion and
undermining of contrary evidence, the fanciful mathematical
pretensions as surrogates for a complex and difficult reality
-- all justified in the name_of policy making prudence.
By any measure of fairness, the EPA draft is not a
scientific analysis. Rather, it reflects a manipulation of
the evidence. Whatever the motivations of the authors, their
methods and conclusions cannot be accepted by anyone with a
modicum of appreciation for the uncertainties involved or for
0
the impartiality that the scientific method demands.
ASSESSMENT OF LUNG CANCER IN ADULTS
While it is cloaked as an open-minded scientific
exercise, the EPA's draft ETS lung cancer risk assessment
reveals itself after careful scrutiny as an apology for a
preconceived notion of what the evidence means. It fails the
test of scientific objectivity for the following reasons.
* The stated null hypothesis is that ETS does not
increase the lung cancer risk of exposed subjects. Yet
studies supporting the null hypothesis are selectively
excluded from the analysis.
* Confidence intervals include values below 1.0 for
RRs in most of the relevant epidemiologic studies, which
implies the probability of either increased or reduced RR
values. Nevertheless, one-tailed probability estimates
are used in the meta-analysis exercise in the draft.

- 6 -
* The document claims consistency of responses and
dose/effects gradients, but this
only by selective
evidence.
* The document
explanations
when in fact
claim can be sustained
elimination of studies with contrary
affirms that no alternative
exist for the alleged excess RRs
observed,
no study has controlled for numerous
suspected factors that have been associated with lung
cancer risk.
* In meta-analysis exercises, tests based on
statistical symmetry apply only to hypothetical
non-biased data and would not hold in the presence of
uncontrolled non-random confounders.
* The document recognizes that social and
environmental differences tend to increase RR values in
Japanese studies, and that the trend of association may
be valid for such studies only. Yet it makes improper use
of Japanese data to estimate RRs and lung cancer
mortality projections for the United States.
SELECTIVE EXCLUSION OF STUDIES
The EPA document justifies the exclusion of the
Varela study from table 3.5 (p. 3-15) and from the
meta-analysis because the proportion of ETS-exposed controls
is not reported. This exclusion is unwarranted, however,
because the raw data "missing" from the written report were

- 7 -
obviously used in the construction of the results published.
This massive study supports the null hypothesis.
Although the 19 studies in table 3.5 are used in the
meta-analytic construction of RRs, statistical support of a
positive association is also contrived from a different set of
selected studies from which all but one of the < 1.0 RR
studies are excluded (table 3-6). The report itself concedes
that the inclusion of studies in the meta-analysis exercise
"... may be subjective." (p. 3-21 bottom). Indeed it is
subjective.
ONE-TAILED PROBABILITIES
The null hypothesis is that ETS exposure does not
affect lung cancer risk. Epidemiologic studies generally show
RR confidence interval bands on both sides of 1.0, which does
not justify rejecting the null hypothesis. The authors of the
EPA document show an understanding of the meaning of such
confidence intervals when they state (p. 3-35 bottom):
"confidence intervals are consistent with a wide range of
possibilities," but they resist the obvious possibilities of
RR values less than 1.0.
The situation mandates the use of two-tailed
probabilities in the statistical analysis of the data. Instead
the EPA document contains statements that must be astonishing
even to an elementary student of statistics, such as (p. 2-2
top): "Statistical significance is evidence that an effect is
at a sufficiently high level to be detected with the data

8
available;-lack of significance only supports the conclusion
that it is below a level that the data have adequately high
power to detect with assurance." And again (section 4.4, p.
4-22): "The data from epidemiologic studies currently
available are evaluated for evidence of an elevated occurrence
of lung cancer associated with ETS exposure." Accordingly, the
document improperly uses one-tailed probability criteria in
several occasions. For instance (p. 3-21, mid-page), the
report states that over half of the 19 case-control studies
have P5 values less than 0.1, when the use of two-tailed
probability shows that to be true for only 4 studies.
STATISTICAL SYMMETRY TESTS
The tests of trend significance based on statistical•
symmetry of meta-analysis data (Figures 3-2 and 3-3 of the
report), are valid under the hypothetical assumption of
unbiased data, namely that non-random confounders ounders are
not at play. Since this assumption cannot be validated and is
actually likely to be false, such tests would also give a
false impression. Publication bias alone would tend to
invalidate the assumption of a symmetrical distribution. The
significance of the Wilcoxon signed-rank test (p. 3-22 bottom)
might be relevant, but the report does not indicate whether in
fact appropriate weight was applied to each study under
two-tailed probability criteria.

- 9 -
DOSE-EFFECT GRADIENTS
The EPA document states (p. 3-38, mid-page): "[w]ith
a consistent upward trend across exposure categories and age
groups that cannot be ascribed to chance alone, one has some
assurance that the sources of variability are not obscuring a
dose-response relationship." This could be true, unless of
course the confounders are non-random ones. As will be seen
later, no study has provided reasonable controls for probable
non-random confounders of lung cancer risk that are
well-described in the literature. Moreover, this assurance
fades when considering that the dose-response gradients of the
epidemiologic studies reviewed are anything but consistent.
In fact, the erratic behavior of such gradients (figure 3.4,
p. 3-28) strongly suggests interferences from non-random
confounders.
The EPA document goes to great lengths to explain
away the absence of a dose-response gradient in Garfinkel
(1981). This is especially evident in the statement at p. 3-35
(bottom): "The statistical evidence supporting an association
between lung cancer incidence and ETS exposure in GARF(coh) is
inconclusive -- it is consistent with either the presence or
absence of a true dose-response relationship." In fact the
evidence tends to support the absence, unless one accepts the
unbelievable rewriting of the meaning of confidence intervals
that follows in the EPA document. The evidence shows that,
with the exception of the weak Correa study (only 8 cases
reported), none of the U.S. epidemiologic studies provides

evidence of an upward dose-response gradient (figure 3-4, p.
3-38).
Thus, one of the fundamental points of this report,
namely that of an upward trend in dose-response (see p. 1-4),
is in fact without foundation.
POTENTIAL CONFOUNDING RISK FACTORS
The EPA draft maintains that "[t]he statistical
results solidly support the conclusion that the observed
association between lung cancer and ETS exposure in
case-control studies is not attributable to chance occurrence "
(p. 3-43, top). And again (4-38 mid-page): "Consideration of
plausible confounding factors and covariables has not produced
an alternative explanation ...." And (4-I mid-page):
Review and analysis . . . of the epidemiologic studies ...
have not indicated a correlate of ETS that may explain the
observed association .
„
The truth, however, is that available ETS
epidemiologic studies controlled for none or very few of the
many common factors that increase or decrease the risk of lung
cancer. Separate studies indicate that such independent
factors may actually cluster and selectively segregate in
families with smokers (Pisani et al., 1986; Whichelow, 1988;
Koo et al., 1988). A partial list of such factors is given in
table 1 below.
