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rhe rationale behind ~be a~emp~s in many countries to
encourage a switch ~rom high-tar to low-tar cigarettes is based on
the presumption tha~ ~he tumorigenic effec~ of tobacco smoke is
mainly a~ribu~able to the particle phase [5]. It would rherefore
seem most appropriate ~o use particulate matter as the constituent
~or estimation of cigarette equivalents. Arundel and his collea~ues
[17| carried out a de~ailed estimation of never smoker ~un~ cancer
risks from exposure to particulate tobacco smoke. They calculated
than, in the US, curren~ smokers have a dai~y retained exposure of
310 mg for men and 249 mg ~or women. In contras˘ the average never
smoker was estimated to have a daily retained exposure o£ 0.07 mg
for men and 0.03 mE for women, equivalent ~o an average of about
1/200~h of a cigarette per day. They further esulma~ed, based on
linear extrapolation from lung cancer risks £n smokers, thac i~ ~he
US in 1980 there would be a uoCal of 12 lung cancer deaths among
n~ver smokers from exposure Co particulate ETS: 8 in men and ~ in
women. This is much lower ~ban ~he EPA estimate of~_Q~ lung cancer
deachs amon~ never smokers from ETS, 500 in men and 1,500 £n women.
(N.B. Arundel et all [17] did not estimate deaths among former
smokers, so comparison wi~h the EPA estimate of 1,060 deaths is not
possible.)
The above estimates indicate that in males never smokers retain
abou~ 0.02~ of the amount of particulate tobacco smoke retained by
current smokers. For females ~he figure is 0.01%o A number of
researchers have used cotinlne, a major metabolize of nicotine, as
BATCo document for Mayo Clinic 27 March 2002

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am arker of relative tobacco smoke exposure. In a large s=udy I
conducted In 1985 £n the UK (18), I found that the corresponding
ranios were about I0 times higher, 0.27% in males and 0.13% in
females. Had cotinlne been used as the index of exposure In Arundel
e._~tal's ealcula=ions, ~hls suggests that about 160 lung cancer
deaths would have been predicted,
lower =ban the EPA estimates.
estlma=es based on eotinlne are valid. In
nicotine itself is not deemed =o be a oarcinogen.
still a full order of magnitude
I~ is doubtful, however, that
the first place,
Secondly, even if
coClnine is used only as an index of smoke uptake, it suffers from
=he major problem that while cotinine is a marker of the lung's
parnicula~e exposure in active smokers, £U is a marker Of ETS gas
phase exposure in nonsmokers. Comparison of cotinine levels in body
fluids of smokers and nonsmokers is therefore misleading.
BATCo document for Mayo Clinic 27 March 2002

3o
~p.l.demiolo~ical approach
There are by now 33 published epidemiological studies oE lung
cancer for ehlch results relating to ETa exposure have been
separately presented for lifelong never smokers. I have recently
prepared an up-to-date assessment of the data from these s~udies
[19], drawing partly on an earlier book [20| in which I examined 28
of =hess studies in detail. The 33 studies I considered included
all those 30 conside=ed by EPA, with the addition of recently
published scudles by Brownson [21] and Stockwell [22}, and a study
by Kabat [23] for which results were only presented at a conference.
[~ £s convenient first =o describe how =he EPA conducted their
risk assessment to reach their estimate of 3,060 lung cancer deaths
attributable ~o ETS. The main steps taken, described in full in
sections 5 and 6 of their report, can be summarized as fo~lows:
(1) Estimate. for never smoking womdn, the relatlve risk of lung
cancer associated with marriage to a smoker (or in some studies
with living w~th a smoker) in each study.
(2) Adjusu the relative risk estimates downward to account for bias
caused by a proporWion of current and former smokers
misrepresenting themselves as ne~er smokers, coupled w[~h the
tendency for smokers preferentially to marry smokers.
(3) Demonstrate, by comb£ni~E adjusted ~ela~ive risk estimates from
the relevant studies, that uhere are stauis~£cally s~gnlflcant
increases in risk ~ relation to ~arriage to/llvlng with a
smoker in the II US studies, in the 5 Japanese studies, in the
~ Hong Kong studies, and in the "2 Greek studies, though nou in
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the 4 West European s~udies or in the & Chinese studies, and
that the overall evidence indicates an associa~ion.
Demonstrate that there is a stronger association of lung cancer
risk with marriage ~o a heavy smoker (or with marriage to a
smoker for a long time) than with marriage to an average
smoker.
(5) Consider various potential confounding factors (history of lung
(6)
(7)
disease, family history of lung disease, heat sources £or
cooking or heating, cooking with oil, occupation, dietary
factors) and couclude that none explains the association
between lung cancer and ET$ exposure.
Classify studies into four "tiers" by a quality assessment, and
show ~ha~ the associations generally remain statistically
si~nlflcant if attention is restricted to studies considered to
be of a better quality.
Use the information in (1) to (6) to determine that there is a
causal relationship, i.e. that a hazard has been identified.
Use an estimate of Z - 1.75 for the relative eotinine level of
never smokers married to a smoker and never smokers married to
a nonsmoker ~o adJus~ US relative risk estimates to a
non-exposed baseline. Thus, relative to a never smoking woman
unexposed ~o ET$ ~he risk of a never smoking woman married to a
nonsmoker is 1.34 and ~he risk oE a never smoking woman married
to a smoker is 1.59. (N.B. the ratio of risks 1.59/1.3& - 1.19
is the relative risk estimate from the I~ US studies, and
ratio of excess risks 0.59/0.3& - I.~5 is the Z-factor
assumed).
BATCo document for Mayo Clinic 27 March 2002

(9) rake an estimate og 9.26, from the A~erican Cancer Society
Cancer ~revention Study, for the risk of current and former
smokers relative to never smokers, and convert it to an
estimate (of 13.8) relative to never smokers unexposed to ETS.
(I0) Use estimates of the total number of lung cancer deaths in US
women in 1985, and estimates of the relative frequency of never
smokers married to nonsmokers, never smokers married to
smokers, and ever smokers, in conjunction with the relative
risks of 1.3&, 1.59 and 13.8 to calculate that there are 6,970
lung cancer dsaths among never smokers, of which &70 are from
ET$ exposure from the spouse and 1,030 from other, non-spousal,
sources of ETa exposure.
(il) Assume estimates of the ~ncreased lung cancer risk in never
smokers in relation to spousal and non-spousal ETS exposure for
women apply equally to men, and calculate that there are 80
deaths from ETS exposure from the spouse and &20 from
non-spousal ETS exposure.
(12) Assume estimates of the increased lun~ cancer risk in never
smokers "in relation to KT$ exposure for women apply to former
smokers of both sexes who have ~Iven up five or more years a~o,
leading to an estimated, f~rther 160 female and i50 male deaths
from spousal ETS exposure and 270 female and aS0 male deaths
from non-spousal ETS exposure.
(13) Sum the numbers for men (I,130) and women (I,930) for never
(2,000) and former (1,060) smokers; or for spousal (860) and
non-spousal (2,200) exposure, ˘o give a total of 3,060
deaths
due to ETS, rounded to 3,000.
BATCo document for Mayo Clinic 27 March 2002

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In my recent review of the evidence I concluded that the
overall evidence from the 33 studies indicated a statistically
significant relationship between lun~ cancer risk in never smoking
women and marriage to (or living with) a smoker. Of 33 relative risk
estimates, unadjusted for covarlates or misclasslflcation of smoking
status, 25 were greater than unity (p<O.Ol) and a "fixed effects"
meta-analysls [24] gave an overall relative risk estimate of 1.17
(95% confidence interval (CI) 1.08-1.27). This estimate was only
marginally changed (to 1.14, 95% CI 1.05-1.23) if one used. where
available, relative risk estimates adjusted for covariates, or if
one used "random effects" mete-analysis (to 1.21, 95% GI
1.09-1.36). "Fixed effects" mete-analysis only takes wlthin-study
variability into account, but "random effects" meta-analysls also
considers between-study variability.
An association could also be seen separately in studies in the
USA, Europe and Asia, estimates (based on unadjusted relative risks
and "fixed effects" meta-analysls) being respectively 1.13 (95% CI
1.00-1.28), 1.&O (95% GI 1.06-1.85), and 1.17 (95% Cl ~.05-1,32).
21 studies provided data on risk in relation to exten~ or
duration of smokin~ by the husband (or cohabitant). Comparing risk
in the most heavily exposed group with that in the overall exposed
group, the former had a higher risk in 16 studies and a lower risk
in only 4, a significant (p<O.05) departure from chance
expectation. Overall the most heavily exposed group had 1.16 times
L~
~O
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the risk o£ the overall exposed group, which suggests ~hat the most
heavily exposed group had 1.35 (- 1.16 x 1.17) times the risk of the
women not married to a s~oker.
So far my conclusions were broadly in llne with those of the
EPA summarized in points (3) and (~) above. However further
exam£natlon of the data revealed a very large number of flaws in the
EPA's argument which totally overturned their conclusions. These
flaws are summarized below:
~sllure to consider
evaluating whether an
vital to eonsLder all
Although,
published,
the spouse,
of risk in
w~rkplace ..and...childhood.....eXposure.
When
association with ETS e~posure exists, it
is
indices of exposure wi~h adequate
data.
in 1986, when a number of the major reviews [3-5] were
there was ~ worthwhile amount of data only on smoking by
this is certainly not true now. There are I~ estimates
never smokers in relation to workplace ETS exposure,
which, when combined, provide no evidence at all o£ an association
with .lung cancer (RR -- 1.02, 95t CI 0.93-1.12). Similarly there are
14 estimates in relation to childhood ETS exposure from the parents,
and again there is no evidence of an association (ER - 0.9&, 95% CI
0.84-I.05). There seem ~o be no strong reasons to believe that
smoking by the spouse is a much better marker of ETS exposure than
is smoking in the workplace o~smoklng by the parent in childhood
[19]. ~t is therefore grossly biassed to do what the EPA did,
namely to conceal from the reader the results for these two
BATCo document for Mayo Clinic 27 March 2002

alternative indices which show no association at all with lung
cancer, and to concentrate solely on the single index, marriage to a
smoker, which does sho~ an association.
F~ure to consider histoloKig˘l type of. lun~ .. cancer. The
association of lung cancer with active smoking is much stronger for
squamous cell cancer than for adenocarcinoma. If, as E~A assume, ETS
is merely a reduced dose of active smoking, one would expect to see
effects, if any, for squamous-cell cancer. In fact the evidence
regarding histological type of lung cancer is conflicting. There are
four studies where the data on spousal smoking seem more consistent
with a relationship with squamous (or small cell) carcinoma, four
studies where the data seem more consistent with'a relationship with
adeno (or large ceil) carcinoma, one study which found a
relationship with both types, and five studies which found no
relationship with either t~e. A major weakness of the EPA report is
that it makes no attempt co compare and contrast results for the two
major t~pes of lung cancer. Consistency is a criterion that EPA cite
for testing causality, but which they do not apply in this context.
Failure to take i~˘? account properly the posslb~itv of
confoundln~. There are three fundamental £1aws in the EPA's
argument, First, they only consider confounding relevant if a single
risk factor can be shown to explain the whole association between
lung cancer and spousal smoking. This is clearly not sensible. More
than one risk factor might confound. Second, when ~rylng to
determine whecher a factor actually elevates lung cancer risk EP~
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restrlcu attentlen vlrqua~ly completely to evidence from" the
ETS/lung cancer studies themselves, ignoring abundant relevant data
from other sources. Third,- they ignore the growing evidence |19,25]
that ETS exposure is associated with exposure to dietary and other
risk factors, and fall to reach the appropriate conclusion that a
nonsmoker married to (or living with) a smoker is generally more
exposed to other risk factors than is a nonsmoker with no smoker in
the household. In a study I conducted recently with my colleagues
Allson Thornton and John Fry [25], I identified 33 llfestyle "risk
factors", i.e. factors generally perceived to be associated with
adverse health consequences, not
cancer risk. Of the 33 factors,
(p<O.001) Increase~ prevalence in
necessarily with increased lung
27 showed a highly significantly
smokers of 20+ cigarettes a day
compared to never smokers, and only 2 a decreased prevalence. 14
of these factors were also significantly (p<0.Ol) increased in never
smokers with a smoker in the household, and non____~ewere significantly
decreased. The factors included low fresh fruit and vegetable
consumptions high fried food consumption, working in an occupation
with a possible cancer risk, low social class, poor eduction, and
high alcohol consumption, all factors linked to an increased lung
cancer risk. Clearly the question is not whether confounding exists,
but what magnitude of bias it causes. Analyses presented elsewhere
[19,25] suggest that confounding could explain a material part of
the reported association of lung cancer with spousal smoking. It
should be noted that the extent to whic~ confounding variables were
taken into account in the .epldemiologioal studies of spousal smokln~
on which the EPA's estimate was based was very limited. Thus over
0
C~
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half ?.he studies where spouse smoking was the index of exposure
failed to restrict attention to married subjects, thereby producing
a serious confoundln~ between potential effects of ET$ exposure and
potential effects of
Furthermore. although
numerous risk factors,
marital status (and its correlates).
many studies reported having recorded
few took any account of these in analysis.
Thus, 31 of the 53 studies did not adjust for dietary factors, one
of these being a study [22]. which actually reported a striking
relationship between diet and lung cancer among never smokers in
another paper [26]!
Failure to eo~re~C, fully.for bias ~ue tq misclassiflcation of active
s~_._~. Adjustment for misclassificatlon is a complex issue
involvin~ a n~mber of assumptions that are not easily justified, and
variables that are not precisely known. In the EPA report, Wells
estimates the bias to be negligible, only increasing the overall
relative risk estimate by a factor o£ about 1.02. However, as
discussed in detail elsewhere |27], there are two major reasons why
this analysis may understate the effect of bias. One reason lles in
the error of applying a mlsclasslflcation rate, estimated from data
virtually all of which comes from North American, European and
Australian populations, to results from lung cancer studies
conducted in Asia. The fact £s that in some countries, such as
~apan, smoking by women is considered socially unacceptable.
Consequently misclassification rates are- likely to be much higher
there. The second reason lies in underestimat£ng the extent of
mlsclassification i~ the countries for which data are available.
CD
~D
BATCo document for Mayo Clinic 27 March 2002
