Lorillard
Comments on Epa Review Drafts 'health Effects of Passive Smoking: Assessment of Lung Cancer in Adults and Respiratory Disorders in Children.' and 'environmental Tobacco Smoke: A Guide to Workplace Smoking Polices'.
Fields
- Author
- Brown, R.C.
- Type
- REPT, OTHER REPORT
- FOOT, FOOTNOTE
- SCRT, SCIENTIFIC REPORT
- FOOT, FOOTNOTE
- Alias
- 87654911/87654915
- Area
- SPEARS,ALEXANDER/EXEC CONF ROOM STORAGE
- Site
- G65
- Request
- R1-004
- R1-048
- R1-132
- R1-048
- Named Person
- Hirayama, T.
- Lowry, A.H.
- Repace, J.L.
- Lowry, A.H.
- Date Loaded
- 05 Jun 1998
- Named Organization
- Epa, Environmental Protection Agency
- Author (Organization)
- Medical Research Council Toxicology Unit
- Litigation
- Stmn/Produced
- Master ID
- 87653565/6821
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Comments on EPA Review drafts uHealth Effects of Passive Smoking:
Assessment of Lung cancer in adults and respiratory disorders in
Children." and "Environmental Tobacco smoke : a guide to workplace
smoking policies".
R.C.Brown, Medical Research Council Toxicology Unit, Woodmansterne
Road, Carshalton, Surrey, UK
Introduction
There is no doubt that exposure to other people's tobacco smoke is irritating and
objectionable; the risk assessment document attempts to show that it is also harmful
while the guide to workplace policies is written to support control of smoking at
work. However the risks from exposure to environmental tobacco smoke (ETS) are
small and, as can be seen from the detailed analysis of the cancer risk felt necessary
in this document, are not universally accepted. It is not my intention to comment on
the mathematics of this analysis or the content and design of the studies analysed
but I do feel that I must comment on some aspects of policy raised by these docu-
ments. The implications of acceptance of this report are profound not only in the
prevention of exposure to ETS but also in determining society's reaction to other
perceived risks.
Respiratory disorders in children
The risk assessment notes that the children of smokers suffer more respiratory
disease than do those of non-smokers. The reason for this phenomenon are not
clear. Among possible causes are exposure to ETS, class differences and exposure
to greater levels of respiratory disease by contact with their smoking parents. There
is enormous scope for more studies on these possibilities and conclusions are not
possible at this point
1

Lung cancer risk in adults
1. It might be appropriate to consider whether meta-analyses are ever appropriate in
making final conclusions as to the existence or absolute magnitude of a risk. This
report is itself a meta-analysis and quotes other similar reports in support of its
findings - yet these are not independent studies being themselves meta-analyses
of the same data. Since sometimes the same authors have contributed to
apparently different reports any agreement is hardly surprising. However often
repeated the results of such studies will not become more powerful. The use of
meta-analysis as a tool for summing small effects rather than for designing new
more powerful surveys will undoubtably be used to justify economies in funding
which will lead to fewer good surveys and less "good science".
2.Little effort is made to identify those studies contributing most authority to the
overall findings. If meta-analysis is to be used it should be supported by
recalculation for all possible subsets of data so as to identify those studies
contributing most to the statistical significance of the overall analysis. If those
studies are themselves flawed then so is the overall analysis. The removal of
outlying results from such calculations is usual and an apposite example can be
seen in Repace & Lowry1 where values for the cigarette equivalent exposure of
passive smokers are omitted for various reasons. Perhaps all meta-analyses
should omit those studies giving extreme values for risk ratios: a genuine effect
will withstand such robust analysis.
3. A great deal is made of the fact that sidestream smoke contains more toxic and
carcinogenic material than does mainstream smoke2 and from the context it is
suggested that this is one reason for the risks claimed to be associated with ETS.
This causes several inconsistencies. If the risk from tobacco smoke in both
--------------------
t.e.g. Repace, J.L & Lowry, A.H. (1990) Risk assessment methodologies in passive smoking. J.Risk
Anal. 10 no.1
2. See particularly 'Environmental tobacco smoke; a guide to workplace smoking policies". p 8
2

smokers and non-smokers is proportional to exposure then there is no need to
invoke this property of ETS. However if passive smokers are affected
disproportionately then the increased potency of ETS can not be the explanation.
Active smokers are also exposed to their own passive smoke, indeed they are at
the centre of any diffusion gradient of smoke and in many cases hold the source
close to their breathing zone between puffs. One must also assume that active
smokers spend less time in smoke free areas than do non-smokers and so are
exposed to more ETS. Correcting the incidence of lung cancer in active smokers
by including their risk from passive smoke would be difficult but should be
attempted before the detailed calculations of risk based on cigarette equivalents.
4. The results leading to the suspected hazardous nature of environmental tobacco
smoke are largely based on exposures occurring in the home - there are few data
concerning possible hazards elsewhere. This is important, because at=home
exposures may differ markedly from public exposure. Hirayama has stressed the
importance of proximity to the source of the smoke - and this is quoted in this
report 1,2. Hirayama appears to regard passive smoking as exposure at a
distance of 1-1.5 metres from the source. Outside the home it is quite likely that
exposures occur at a far greater distance and that the substances and
concentrations to which anybody is exposed in the workplace or public building
differ markedly from those in a small (Japanese) house shared with a smoker. If
this is the case (and the question is worth study) it is clearly inappropriate to
utilise studies based on at-home exposures as the source for the adoption of
control measures in other places.
In most cases the identification of a risk leads to control of the exposure causing
that risk and, if possible, any control of the toxicant would then be widened to
other related, exposures. This is not the case in this study where the supposed
demonstration of hazard in one setting would be used to justify the control of
1. Health Effects of passive smoking: assessment of lung cancer in animals and respiratory disorders
in children. p 3-39: OD
Q
2. Hirayama, T.(1984) Prev.Med. 13:680-690 CCM11
3

quite different exposures leaving the original (domestic) exposures alone. Surely
the logical consequence of accepting this report should be the health risk
warnings on packets such as "smoking can damage your spouse's health" rather
than the concentration on control of workplace exposures.
5. While accepting the theoretical point that there may be no threshold for
carcinogenic effects this is not a practical view point for the control of
carcinogens: in any case would not be true for other health effects. Most
authorities would doubt the wisdom of attempting to control a material without
suitable methods for monitoring and measuring exposure. If suitable methods do
not yet exist then attempts at control are premature. In the "guide to workplace
policies" work on suspended particulates and other measures of smoke exposure
are discussed but again the results quoted are mainly from studies of domestic
exposures and it is notable that proximity to source is not mentioned explicitly as
a dose determinant. However in the review document 1 the importance of
proximity to source and the small living spaces enjoyed by the Japanese are
invoked to explain Hirayama's results. Despite this no attempt is made to
compare these domestic exposures to those in the workplace or suggest control
levels. Surely an action level of zero is neither possible nor practical.
6. If we now accept that the resolution of epidemiological methods is such that
exposures with relative risks of under 1.5 should be prevented then many other
materials may have to come under legislative control. Has any previous control
measure been adopted with this level of increased risk?
7. A list of the toxic materials in ETS, some animal and other results with these
components, and the possible use of these results to model the effects of ETS
are given - does this add to the analysis in this document? Most of the
components mentioned are widespread and indeed this list of components of
tobacco smoke could (with the exception of nicotine) be equally applied to most
smokes, exhaust fumes or pyrolysis products. I would recommend much more
1.Effects of passive smoking: assessment of lung cancer in animals and respiratory disorders in
children. p 3-39:
-4-

research on the effects of these compounds both alone and in combinations but
the present list must mean that the suggested controls should apply to other
sources of airborne carcinogens such as car exhausts, bonfires, barbecues etc.
If the EPA accept that there should be zero emission of these materials from
tobacco smoke how will they avoid pressure to eradicate (not control) other
emissions?
8. The acceptance of this report could lead to the attribution to passive smoking of
many lung cancers that are in fact due to other as yet unidentified causes. Such
attribution will lead to less effort being put into the identification of any novel
hazards leading to lung cancer. This has happened with other materials.
Mesothelioma has been usually attributed to asbestos exposure and as with ETS
there is an almost universal exposure to asbestos this has made it difficult to
identify any other causes for this rare tumour. There is now reason to believe that
perhaps half of the mesotheliomas are not associated with asbestos and the
problems caused by firmly held preconceptions can be seen by the exhaustive
search for asbestos exposure when endemic mesotheliomas were found in
Turkey~ .
--------------------
1.Rohl, A.N.. Langer A.M., Moncure, G.,Selikoff, U., & Fischbein, A. Science 216: 518-520
-5
