Lorillard
Comments on the Draft Epa Document Environmental Tobacco Smoke A Guide to Workplace Smoking Policies
Fields
- Author
- Lewis, T.R.
- Type
- SCRT, SCIENTIFIC REPORT
- BIBL, BIBLIOGRAPHY
- Alias
- 87654680/87654688
- Area
- SPEARS,ALEXANDER/EXEC CONF ROOM STORAGE
- Site
- G65
- Request
- R1-004
- R1-041
- R1-132
- R1-041
- Named Person
- Haley
- Janerich
- Melius
- Robertson
- Janerich
- Date Loaded
- 05 Jun 1998
- Named Organization
- Acute + Subacute Toxicology Section
- American Society of Heating Refrigeratio
- Epa, Environmental Protection Agency
- Experimental Toxicology Branch
- Health Effects Research Lab
- Healthy Buildings Intl
- Mi State Univ
- Natl Air Pollution Control Administratio
- Niosh, Natl Inst for Occupational Safety & Health
- TI, Tobacco Inst
- Toxicology + Microbiology Division
- American Society of Heating Refrigeratio
- Litigation
- Stmn/Produced
- Master ID
- 87653565/6821
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- UCSF Legacy ID
- ovr21e00
Document Images
September 27, 1990
Comments on the Draft EPA Document
Environmental Tobacco Smoke
A Guide to Workplace Smoking Policies
by Trent R. Lewis, Ph.D.
I have been asked by The Tobacco Institute to
comment on the draft document entitled "Environmental Tobacco
Smoke: A Guide to Workplace Smoking Policies." I am
currently a private consultant on occupational, environmental
and toxicologic issues. I received a Ph.D. from Michigan
State University in 1961 in animal nutrition with minors in
biochemistry, physiology and bacteriology.
My professional career in toxicology began in 1963
as Chief, Chronic Exploratory Toxicology Unit with the
National Air Pollution Control Administration, responsible for
the development, design, conduct and supervision of
toxicologic studies addressing health hazards posed by air
pollutants, notably those generated by automotive emissions.
From 1971-1987, I was employed by the National Institute for
Occupational Safety and Health, initially as Chief, Acute and
7
Subacute Toxicology Section, and in 1907 as Chief,
Experimental Toxicology Branch, Division of Biomedical and
Behavioral Science. From 1987 to 1989, I was employed at EPA
as Director, Toxicology and Microbiology Division, Health
Effects Research Laboratory. During this period I conducted
and supervised research and agency programs regarding health

Response to the Draft EPA document
ETS: Guide to Workplace Smoking Policies
Trent R. Lewis, Ph.D.
Page 2
hazards posed by toxic agents in the workplace and ambient
air, soil and water, including automotive emissions,
industrial ketones and 2-nitropropane. Through this
professional experience, I have developed broad knowledge of
environmental toxicology, risk assessment, and other
approaches to determining safe levels of human exposures to
chemical substances and agents, and the application of these
disciplines to risk management and the development of
regulatory policy.
A complete description of my education, credentials
and qualifications are included in my curriculum vitae, a copy
of which is attached.
Introduction
In the Introduction to the draft Policy Guide, the
sweeping statement is made that "ETS is one of the most
widespread and harmful indoor air pollutants." In light of
the available evidence, this conclusion appears wholly
inaccurate. The National Institute for Occupational Safety
and Health (Melius et al., 1984) and a private corporation,
Healthy Buildings International, Inc. (Robertson, 1990), have
investigated hundreds of public and private buildings in
response to complaints by the occupants. In only two to three
percent of these field investigations was environmental
tobacco smoke ("ETS") found to be a major contributory factor
to the air quality problems that had been identified.

Response to the Draft EPA document
ETS: Guide to Workplace Smoking Policies
Trent R. Lewis, Ph.D.
Page 3
The Introduction also states that "[u]nless there is
evidence to the contrary, EPA believes that any exposure to a
cancer causing agent -- regardless of level -- increases the
risk of cancer." That fundamental premise is controversial
and by no means generally accepted. It also is not sufficient
to support the extraordinarily broad policy recommendations
contained in the draft Guide. For reasons that are not
explained, the draft fails to discuss the range of possible
policies and management practices that might be adopted
regarding ETS, and the actual costs and benefits of those
actions. These cost-benefit considerations typically are the
most important issues facing federal agencies in setting
"acceptable" exposure limits for recognized human or animal
carcinogens in air, food and water.
A very substantial percentage of adult Americans are
smokers. In setting policy that would affect the daily life
of such a large segment of the public, and potentially cause
dislocation and disruption in the workplace and public
facilities, a balanced assessment of the range of policy
options available and their costs/benefits is essential.
Instead, the draft Guide appears to be driven by a generalized
antipathy to smoking and a value judgment that the practice
should be discouraged or eliminated regardless of exposure
level or social cost.
From the total weight of evidence available, it is .
also premature, if not impossible, to conclude that ETS is a

Response to the Draft EPA document
ETS: Guide to Workplace Smoking Policies
Trent R. Lewis, Ph.D.
Page 4
occupational (workplace) carcinogen. The clear majority of
the individual epidemiological studies have failed to
demonstrate a statistically significant relative risk and
those studies that were statistically significant were of
non-U.S. populations with radically different cultures and
lifestyles. Most significantly, the one substantial
epidemiological study that has addressed workplace exposure to
ETS has very recently reported "no evidence of an adverse
effect of environmental tobacco smoke in the workplace."
(Janerich, et. al., 1990).
Part I: Environmental Tobacco Smoke: "The Problem"
Although many comments could be made on technical
points presented in Chapter 1, I will confine my comments to
issues of particular relevance to my areas of expertise.
First, it is inaccurate and misleading to suggest that
substances originating from ETS and absorbed into the body
tend to have a longer systemic residency time than identical
substances drawn directly from mainstream smoke in active
smokers (bottom p. 7). This difference has been reported only
for nicotine (Haley et al., 1989); no similar data exist for
other chemical substances in mainstream smoke versus ETS.
Second, "toxins and irritants" are inaccurately portrayed in
the text and tabular formats (pp. 9-10). The title of the
Table on page 10 is misleading to lay readers who may be led
to believe that each chemical substance listed is both toxic
and carcinogenic. Nicotine, carbon monoxide, catechol and

Response to the Draft EPA document
ETS: Guide to Workplace Smoking Policies
Trent R. Lewis, Ph.D.
Page 5
ammonia are not carcinogenic and are toxic only after
exceeding a threshold concentration or dose. The same is true
for hydrogen cyanide, which is referred to in the text. It is
erroneous to present the toxicological descriptions for
hydrogen cyanide and ammonia as written since there is no
likelihood that the human effects stated would ever result
from the minimal levels associated with exposure to ETS.
I have similar comments with respect to Chapter 2.
First, while it may be true that "many people spend up to 90%
of their time indoors," people do not spend 100% of their
indoor time at the worksite. Second, under "Defining
Exposure," two separate definitions are provided for extent of
exposure and dose. Only the latter -- dose -- is germane from
a health or toxicologic perspective. Extent encompasses only
the duration of exposure, whereas dose encompasses both the
duration of exposure and the amount of a substance that is
inhaled and retained. Third, page 13 describes benzene as a
"surrogate" for ETS that can be hazardous to those exposed to
ETS. In fact it is neither. The principal source of exposure
to benzene is petroleum-based materials, notably gasoline and
refined petroleum solvents. There is no evidence from smokers
or nonsmokers that benzene, at the miniscule concentrations
found in ETS, has induced leukemia or blood dyscrasias, the
major chronic health hazards posed by benzene.

Response to the Draft EPA document
ETS: Guide to Workplace Smoking Policies
Trent R. Lewis, Ph.D.
Page 6
Part II. Environmental Tobacco Smoke: "The Solution"
Consistent with the tone set in the Introduction,
Part II gives an unbalanced and exaggerated picture of ETS in
relation to the general problem of poor indoor air quality in
U.S. workplaces. NIOSH (1984) found that almost 80% of indoor
air quality problems were related to three primary factors
other than ETS. The first of these was inadequate
ventilation; this dominant component accounted for 48% of the
problems. The second factor, accounting for 18% of the
problems, was exposure to a toxic substance originating from
sources related to equipment or specific workpractices within
the building (e.g., copy machines, use of pesticides,
humidification agents, or cleaning supplies). The third major
problem, identified in 11% of the investigations, was
contamination from sources external to the building, (e.g.,
motor vehicle exhaust, boiler gases, previously exhausted air,
and construction dust). In only 4 of 203 investigations was
ETS found to play a role in the symptoms experienced by
complainants. Likewise, Healthy Buildings International, Inc.
(Robertson, 1990) found ETS to be a major contributing factor
in only 2% of its investigations. From these data, the
obvious conclusion is that the elimination of ETS from
worksites will have a very minor impact on improving indoor ~
air quality even in buildings where air quality problems have ~
~
been identified. ~
GD
G11

Response to the Draft EPA document
ETS: Guide to Workplace Smoking Policies
Trent R. Lewis, Ph.D.
Page 7
By focusing undue attention on ETS, the draft Policy
Guide neglects the single most important step that can be
taken to ensure healthy workplace air quality: provide
adequate ventilation (NIOSH, 1984; Robertson, 1990). The
American Society of Heating, Refrigeration and Air
Conditioning Engineers (ASHRAE, 1989) recommends a ventilation
rate of 20 cfm per person (with 15 cfm as an absolute minimum)
for offices, and higher rates for high emission locations,
such as printing and copying rooms. In the industrial
setting, supplemental ventilation may be required to reduce
industrial emissions, including local exhaust ventilation
where necessary. The draft Policy Guide as written may well
have the effect of delaying compliance with ASHRAE standards
by portraying smoking prohibitions as a "cure-all" for indoor
air quality.
Part III: Case Studies
Part III's discussion of workplace smoking policies
and "case studies" is limited to offices and public buildings
and likewise appears to be premised on the assumption that,
contrary to results of the studies discussed above, ETS is the
sole source of indoor air problems in those settings. The
Chapter also simply ignores the fact that industrial settings
present air quality problems that are broader in scope and
often more environmentally complex and severe than office
locations. As with Part.II, the mistaken premise of Part III

Response to the Draft EPA document
ETS: Guide to Workplace Smoking Policies
Trent R. Lewis, Ph.D.
Page 8
appears to be that prohibition of smoking is a "magic
solution" to indoor air quality.
Conclusion
The overall impression created by the draft Policy
Guide is that elimination of ETS would effectively cure nearly
all indoor air quality problems. Yet the available data
indicate that, when specific instances of known problems are
investigated, ETS plays an insignificant role. Exposure to
the specific compounds cited by the draft Policy Guide in
relation to ETS, such as polycyclic aromatic hydrocarbons and
nitrosamines, is also well known to result from occupational
environments (coking operations, foundry casting, diesel
engines, etc.), office environments (printing and copying
equipment, off-gassing by furnishings), residential
environments (cooking and heating), and the ambient air
(vehicle exhaust, fossil fuel power plants, etc.) The draft
Policy Guide relies on inadequate data to make an incorrect
and unjustifiable policy statement that prohibition of smoking
in the workplace is the solution to indoor air quality
problems. The unfortunate result may well be that remedial
steps addressing serious exposures to known hazards (in
contrast to ETS) are deferred or ignored.

Response to the Draft EPA document
ETS: Guide to Workplace Smoking Policies
Trent R. Lewis, Ph.D.
Page 9
References
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J. Indoor air quality--the NIOSH experience. Ann. Am.
Conf. Gov. Ind. Hyg. 10: 3-7, 1984.
3. Robertson, G., Indoor pollution: sources, effects and
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6. American Society of Heating, Refrigeration, & Air
Conditioning Engineers, Standard 62-1989. Ventilation
for acceptable indoor air quality, 1989.
