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 Collections under which this article appears: Environmental
Issues Smoking
Ischaemic
heart disease Cancer: lung
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1 School of Public Health, University of California, Los Angeles, CA 90095-1772, USA, 2 Department of Preventive Medicine, State University of New York, Stony Brook, NY 11794-8036, USA
Correspondence to: J E Enstrom jenstrom@ucla.edu
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Abstract |
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Design Prospective cohort study covering 39 years.
Setting Adult population of California, United States.
Participants 118 094 adults enrolled in late 1959 in the American Cancer Society cancer prevention study (CPS I), who were followed until 1998. Particular focus is on the 35 561 never smokers who had a spouse in the study with known smoking habits.
Main outcome measures Relative risks and 95% confidence intervals for deaths from coronary heart disease, lung cancer, and chronic obstructive pulmonary disease related to smoking in spouses and active cigarette smoking.
Results For participants followed from 1960 until 1998 the age adjusted relative risk (95% confidence interval) for never smokers married to ever smokers compared with never smokers married to never smokers was 0.94 (0.85 to 1.05) for coronary heart disease, 0.75 (0.42 to 1.35) for lung cancer, and 1.27 (0.78 to 2.08) for chronic obstructive pulmonary disease among 9619 men, and 1.01 (0.94 to 1.08), 0.99 (0.72 to 1.37), and 1.13 (0.80 to 1.58), respectively, among 25 942 women. No significant associations were found for current or former exposure to environmental tobacco smoke before or after adjusting for seven confounders and before or after excluding participants with pre-existing disease. No significant associations were found during the shorter follow up periods of 1960-5, 1966-72, 1973-85, and 1973-98.
Conclusions The results do not support a causal relation between environmental tobacco smoke and tobacco related mortality, although they do not rule out a small effect. The association between exposure to environmental tobacco smoke and coronary heart disease and lung cancer may be considerably weaker than generally believed.
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Introduction |
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Although these reviews come to similar conclusions, the association between environmental tobacco smoke and tobacco related diseases is still controversial owing to several limitations in the epidemiological studies.9–14 Exposure to environmental tobacco smoke is difficult to measure quantitatively and therefore has been approximated by self reported estimates, primarily smoking history in spouses. Confounding by active cigarette smoking is so strong that the association with environmental tobacco smoke can only be evaluated among never smokers. The relation between tobacco related diseases and environmental tobacco smoke may be influenced by misclassification of some smokers as never smokers, misclassification of exposure status to environmental tobacco smoke, and several potential confounders. It is also unclear how the reported increased risk of coronary heart disease due to environmental tobacco smoke could be so close to the increased risk due to active smoking (30% and 70%, respectively), since environmental tobacco smoke is much more dilute than actively inhaled smoke.
Most epidemiological studies have found that environmental tobacco smoke has a positive but not statistically significant relation to coronary heart disease and lung cancer. Meta-analyses have combined these inconclusive results to produce statistically significant summary relative risks.4–8 However, there are problems inherent in using meta-analysis to establish a causal relation.9–14 The epidemiological data are subject to the limitations described above. They have not been collected in a standardised way, and some relative risks have been inappropriately combined. Because it is more likely that positive associations get published, unpublished negative results could reduce the summary relative risks. Also, the meta-analyses of coronary heart disease omitted the published negative results from the large American Cancer Society cancer prevention study (CPS I).10 11 We have extended the follow up for the California participants in this cohort, analysed the relation between environmental tobacco smoke and tobacco related diseases, and addressed concerns about this study.
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Methods |
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Follow up
Long term follow up was undertaken at the
University of California at Los Angeles on all 118 094 participants
from California. This is described in detail elsewhere and summarised
in table
1. 18 The
participants were matched several times with the California death
file and the social security death index on the basis of their name
and other identifying variables.18 19
Overall, 79 437 deaths were identified up to 31 December 1998, and
the underlying cause was obtained from the California death file
and death certificates for 93% (73 876) of these deaths.
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Participants were also matched with information given on their California driver's licence, based primarily on name, date of birth, and height. We obtained the address given during the 1990s for 21 897 participants who were not known as dead as of 1999, and these participants were assumed to be alive in 1999. Of the remaining participants in the study's master database, 6845 were withdrawn from further follow up as of September 1972 because their complete name was not retained, and 9915 were lost to follow up as of 1999 because their vital status was unknown.
To assess the current status of surviving cohort members, in mid-1999 we sent out a two page questionnaire on smoking and lifestyle to those participants with an address for 1995 or later on their driver's licence. Overall, 2290 of 5275 men (43.4%) and 4869 of 10 738 women (45.3%) completed the questionnaire. Responses to name, date of birth, and height on the questionnaire confirmed that over 99% of the respondents had been accurately located.
The follow up period was from time of entry to the study (1 January to 31 March 1960) until death, withdrawal (date last known alive), or end of follow up (31 December 1998). The participants were aged 30-96 years at enrolment. We excluded the few person years of observation and the 36 deaths during 1959. The underlying cause of each death was assigned according to the international classification of diseases (seventh, eighth, or ninth revisions). Coronary heart disease was defined as 420 (ICD-7) during 1960-7, 410-4 (ICD-8) during 1968-78, and 410-4 (ICD-9) during 1979-98, lung cancer was defined as 162-3 (ICD-7), 162 (ICD-8), and 162 (ICD-9), and chronic obstructive pulmonary disease was defined as 241, 500-2, and 527.1 (ICD-7), 490-3 (ICD-8), and 490-6 (ICD-9). For the analysis of environmental tobacco smoke we selected the 35 561 participants who had never smoked as of 1959 and who had a spouse in the study with known smoking habits.
Statistical analysis
The independent variable used for
analysis was exposure to environmental tobacco smoke based on smoking
status of the spouse in 1959, 1965, and 1972. Never smokers married
to current or former smokers were compared with never smokers married
to never smokers. The 1959 never smokers were defined as those who
had never smoked any form of tobacco as of 1959. The 1965 never
smokers were defined as 1959 never smokers who did not smoke
cigarettes as of 1965. The 1972 never smokers were defined as 1959
never smokers who did not smoke cigarettes as of 1965 and 1972.
The 1959/1999 never smokers were defined as 1959 never smokers
who had never smoked cigarettes as of 1999. Never smokers married
to a current smoker were subdivided into categories according
to the smoking status of their spouse: 1-9, 10-19, 20, 21-39,
40 cigarettes consumed
per day for men and women, with the addition of pipe or cigar usage
for women. Former smokers were considered as an additional
category.
We calculated the age adjusted relative risk of death and 95%
confidence interval as a function of smoking status of the
spouse by using Cox proportional hazards regression.18 20
A fully adjusted relative risk was calculated by using a model
that included age and seven potential confounders at baseline:
race (white, non-white), education level (< 12, 12, > 12
years), exercise (none or slight, moderate, heavy), body mass index
(< 20, 20-22.99, 23-25.99, 26-29.99, 30), urbanisation (five
population sizes), fruit or fruit juice intake (0-2, 3-4, 5-7 days a
week), and health status (good, fair, poor, sick). Analyses were
carried out for all participants and for healthy participants (those
with no history of cancer, heart disease, or stroke at baseline). The
relative risk was also calculated for current cigarette smokers
(cigarettes only) as a function of number of cigarettes consumed per
day for the entire cohort.18 For
reference, the age adjusted death rate has been calculated by cause
of death for all never smokers.18
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Results |
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The smoking status of spouses as of 1959 was related to three self reported measures of exposure to environmental tobacco smoke as of 1999 (table 4). Particularly for women, there was a clear relation between smoking status of spouses as of 1959 and self reported measures in 1999 of having lived with a smoker, having lived with a smoking spouse, and a positive answer to the question "In your work or daily life, are (were) you regularly exposed to cigarette smoke from others" Also, the percentage of participants currently married as of 1999 declined substantially with the smoking status of the spouse, owing to increased widowhood. Smoking history of the spouse as assessed in 1999 was strongly related to exposure to environmental tobacco smoke as of 1999 for both men and women (table 5).
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Misclassification of exposure and smoking status
Although
there was substantial misclassification of environmental tobacco
smoke exposure status from 1959 to 1999, it was less for those never
smokers aged 50 or over at enrolment (see table 4),
never smokers defined in 1972 (data not shown), and never
smokers defined in 1999 (see table 5).
Misclassification of exposure status produces a measured relative
risk that is closer to 1.0 than the true relative risk.8 13 The
extent of misclassification from 1959 to 1999 could not obscure a
true association with a relative risk of about 1.3, if it exists,
among women, but it could largely obscure this association among men.
However, this level of misclassification, which is based on the
changes that occurred over 40 years among the younger than
average 1999 respondents, exaggerates the true level of
misclassification that occurred among the cohort as a whole,
particularly during short follow up periods.
Essentially all 1959 never smokers remained never smokers on the basis of smoking status reported in 1965, 1972, and 1999 (table 6). Of those who reported a history of smoking in 1999, most had smoked no more than 10 cigarettes per day for a few years, and most had quit smoking before 1960. This indicates only a small degree of misclassification of smoking status. Some bias exists in the misclassification of smoking status among the 1959 never smokers, because the percentage who smoked in the 1965 and 1972 surveys was greatest among those with the highest levels of smoking in spouses. This bias produces a measured relative risk that is greater than the true relative risk, but by a negligible amount for this level of bias.8 13
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Effect of exposure to environmental tobacco
smoke
Exposure to environmental tobacco smoke was not
significantly associated with the death rate for coronary heart
disease, lung cancer, or chronic obstructive pulmonary disease in
men or women (tables 7 and 8). This was true
for all 1959 never smokers and 1959 never smokers aged 50 or over at
enrolment followed during 1960-98 and for 1972 never smokers
followed during 1973-98. The relative risks were slightly reduced
after adjustment for seven confounders. Results were essentially
unchanged among the healthy participants only (data not shown).
The relative risks were consistent with 1.0 for virtually every
level of exposure to environmental tobacco smoke, current or
former. Only the relative risks for chronic obstructive pulmonary
disease suggested an association. An environmental tobacco
smoke index based on seven or eight levels of smoking in a
spouse yielded a relative riskof about 1.0 for each level of
change and no suggestion of a dose-response trend.
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In addition, analyses for coronary heart disease were performed for three short follow up periods with presumably smaller misclassification errors. All relative risks for coronary heart disease were consistent with 1.0 for the follow up periods of 1960-5, 1966-72, and 1973-85 for never smokers defined as of 1959, 1965, and 1972 (table 9). In particular, the relative risk for current smoking in a spouse was not increased, and there were no trends based on the environmental tobacco smoke index.
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As expected, there was a strong, positive dose-response relation between active cigarette smoking and deaths from coronary heart disease, lung cancer, and chronic obstructive pulmonary disease during 1960-98 (table 1010). These relative risks were consistent with those for the full CPS I cohort until 1972.15 17 As it is generally considered that exposure to environmental tobacco smoke is roughly equivalent to smoking one cigarette per day,4 we extrapolated the relative risk due to exposure to environmental tobacco smoke from the relative risks for smoking 1-9 cigarettes per day. These extrapolated relative risks were about 1.03 for coronary heart disease and about 1.20 for lung cancer and chronic obstructive pulmonary disease. Based on these findings, exposure to environmental tobacco smoke could not plausibly cause a 30% increase in risk of coronary heart disease in this cohort, although a 20% increase in risk of lung cancer and chronic obstructive pulmonary disease could not be ruled out.
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Discussion |
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Strengths of study
CPS I has several important strengths:
long established value as a prospective epidemiological study, large
size, extensive baseline data on smoking and potential confounders,
extensive follow up data, and excellent long term follow up. None
of the other cohort studies on environmental tobacco smoke has
more strengths, and none has presented as many detailed results.
Considering these strengthsas a whole, the CPS I cohort is one
of the most valuable samples for studying therelation between
environmental tobacco smoke and mortality.
Concern has been expressed that smoking status of the spouse as of 1959 does not accurately reflect total exposure to environmental tobacco smoke because there was so much exposure to non-residential environmental tobacco smoke at that time.6 The 1999 questionnaire showed that the smoking status of spouses was directly related to a history of total exposure to environmental tobacco smoke. It also showed that the extent of misclassification of exposure was not sufficient to obscure a true association between environmental tobacco smoke and coronary heart disease among women (see tables 4 and 5).
Our methodology and results are fully described because of concern that the earlier analysis of coronary heart disease in CPS I 10 was flawed by author bias owing to funding by the tobacco industry.4 Our results for coronary heart disease and lung cancer are consistent with those of most of the other individual studies on environmental tobacco smoke,4–8 including the results for coronary heart disease and lung cancer in the full CPS I.10 16 Moreover, when our results are included in a meta-analysis of all results for coronary heart disease, the summary relative risks for current and ever exposure to environmental tobacco smoke are reduced to about 1.05, indicating a weak relation.
Widowhood was strongly correlated with smoking status of spouses, owing to the reduced survival of smokers. Since widowers have higher death rates than married people,22 23 controlling for widowhood would be expected to reduce the relative risks in this and other studies of smoking in spouses. The precise effect of widowhood due to smoking in spouses still needs to be determined, but it may partially explain the positive relative risks found in other cohorts.
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Contributors: JEE conceived the study and obtained funding, conducted the extended follow up, analysed the data, and drafted the manuscript; he will act as guarantor for the paper. GCK contributed to the follow up questionnaire, advised on the data analysis and interpretation, and contributed extensively to the manuscript.
Funding: The American Cancer Society initiated CPS I in 1959, conducted follow up until 1972, and has maintained the original database. Extended follow up until 1997 was conducted at the University of California at Los Angeles with initial support from the Tobacco-Related Disease Research Program, a University of California research organisation funded by the Proposition 99 cigarette surtax (www.ucop.edu/srphome/trdrp). After continuing support from the Tobacco-Related Disease Research Program was denied, follow up through 1999 and data analysis were conducted at University of California at Los Angeles with support from the Center for Indoor Air Research, a 1988-99 research organisation that received funding primarily from US tobacco companies.24
Competing interests: In recent years JEE has received funds originating from the tobacco industry for his tobacco related epidemiological research because it has been impossible for him to obtain equivalent funds from other sources. GCK never received funds originating from the tobacco industry until last year, when he conducted an epidemiological review for a law firm which has several tobacco companies as clients. He has served as a consultant to the University of California at Los Angeles for this paper. JEE and GCK have no other competing interests. They are both lifelong non-smokers whose primary interest is an accurate determination of the health effects of tobacco.
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| Collections under which this article appears:Environmental
Issues Smoking
Ischaemic
heart disease Cancer: lung
|
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