Lorillard
Review of: Environmental Tobacco Smoke A Compendium of Technical Information
Fields
- Author
- Turner, S.
- Alias
- 88772585/88772596
- Type
- REPT, OTHER REPORT
- BIBL, BIBLIOGRAPHY
- Area
- CROUSE,WILLIAM/BASEMENT GMP
- Site
- G10
- Named Organization
- Coast Guard
- Customs + Excise
- Epa, Environmental Protection Agency
- Government Services Administration
- Healthy Buildings Intl
- Hhs, Dept of Health and Human Services
- Niosh, Natl Inst for Occupational Safety & Health
- Social Security Administration
- Supreme Court
- Un, United Nations
- Ashrae
- Named Person
- Lowry
- Repace
- Date Loaded
- 12 Feb 1999
- Master ID
- 88772371/2597
- 88772371-2597 United States Environmental Protection Agency Environmental Tobacco Smoke: A Compendium of Technical Information Comments of the Tobacco Institute 900205 Reviewers' Statements
- 88772372-2379 Comments on Chapter 3
- 88772380-2396 Review of: Environmental Tobacco Smoke A Compendium of Technical Information
- 88772397-2403 Reactions to Environmental Tobacco Smoke: A Compendium of Technical Information Chapter 4: Environmental Tobacco Smoke and Cancer
- 88772404-2418 Comments on Environmental Tobacco Smoke: A Compendium of Technical Information Chapter 4: Environmental Tobacco Smoke and Cancer
- 88772419-2433 Chapter 4: Environmental Tobacco Smoke and Cancer - Environmental Tobacco Smoke: A Compendium of Technical Information
- 88772434-2442 Statement
- 88772443-2466 Critique of the Report Entitled Environmental Tobacco Smoke: A Compendium of Technical Information U.S. Environmental Protection Agency Chapters 5-8
- 88772467-2481 Environmental Tobacco Smoke: A Compendium of Technical Information Technical Review
- 88772482-2494 Review of: Environmental Tobacco Smoke A Compendium of Technical Information
- 88772495-2500 Comments by Dr. Guy B. Oldaker III on Chapter 5 Measuring Exposure to Environmental Tobacco Smoke
- 88772501-2504 Comments with References on 'measuring Exposure to Environmental Tobacco Smoke'
- 88772505-2512 Comments by Dr. Guy B. Oldaker III on Chapter 6 Exposures to Air Pollutants
- 88772513-2530 Comments by Dr. Guy B. Oldaker III on Chapter 7 Exposure Assessment in Passive Smoking
- 88772531-2533 Comments on Chapter 7: Exposure Assessment in Passive Smoking
- 88772534-2540 Review of Chapter 8 by D. Hoffmann, K.D. Brunnemann, and N. J. Haley of the Draft Compendium of Technical Information on Ets Edited by the Environmental Protection Agency
- 88772541-2553 Critique of Environmental Tobacco Smoke: A Compendium of Technical Information Chapter 9: the Effects of Passive Smoking and Day Care on Respiratory Illnesses in Children
- 88772554-2572 Evaluation of Appendix 10: Economic Justification for No Smoking Policies at the Worksite
- 88772573-2584 Economic Justification for Worksite Smoking Policies
Related Documents:
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REVIEW OF:
ENVIRONMENTAL TOBACCO SMOKE
A COMPENDIUM OF TECHNICAL INFORMATION
by
Simon Turner,
Healthy Buildings International, Inc.
Introduction
Healthy Buildings Internatioaal, Inc. (HBI) is a
company that specializes in the study 3nd assessment of indoor
air pollution.. Since we incorporated in 1981, we have studied
in excess of 80 million square feet of buildings throughout
the world, perhaps confirming us as the most experienced
private company in that field. HBI seeks to identify the
causes of indoor air quality problems -- the "sick building
syndrome" -- and to recommend remedial steps. Our experiences
are attracting widespread interest in the professional arena
of those truly interested in indoor air quality. Clients
include major banks, insurance companies, property developers,
hospitals, colleges, and government agencies, including the
U.S. Department of Health and Human Services, Social Security
Administration, Longworth Congressional Building, Supreme
Court, Government Services Administration Regional Head-
quarters, United Nations Buildings in New York, Customs and
Excise and Coast Guard Buildings.
We were asked to comment upon the document entitled
"Environmental Tobacco Smoke: A Compe!ndium of Technical
Information" based upon our extensive experience with indoor
air quality problems. In addition to a number of specific
substantive flaws contained in the document, this compendium

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on environmental tobacco smoke (ETS) sanctioned by a body such
as the U.S. Environmental Protection Agency (EPA) concerns us
in that this single-minded focus on one pollutant, unique in
EPA's policies on indoor air, will give the public the
impression that its removal will solve all indoor air
problems, thus giving an entirely false sense of security.
We frequently investigate buildings on account of
complaints from occupants with symptoms.such as-eye and nose
irritation, fatigue, coughing, rhinitis, nausea, headaches,
sore throats and general respiratory problems. It is
frequently assumed by our clients that these symptoms are due
to ETS. However, it is clear that identical symptoms may be
found in individuals exposed to formaldehyde, sulphur oxides,
ammonia', oxides of nitrogen, and ozone. In addition, similar
symptoms are reported by those individuals with allergies to
specific fungi such as aspergillus, cla3osporium, and
penicillium, among others, as well as to miscellaneous
bacterial aerosols. Overlapping symptoms also can be caused
by exposure to household dusts, cotton fibers, fiberglass
fragments, etc. Low relative humidities create similar
problems and are on the increase.
Surprisingly, after a detailed, scientific
evaluation of these buildings, we have determined high levels
of environmental tobacco smoke to be the immediate cause of
indoor air problems in only three percent of the 412 major
U.S. buildings investigated by HBI between 1981 and 1989.
This result has been corroborated. In a similar study of 203

buildings from 1978 to-1983; the Naticnal Institute-for
Occupational Safety and Health (NIOSH) found that
only four_ of
the buildings studied (two percent) hz.d indoor air quality
problems attributable to high concentrations of ETS.
significantly, in those few cases where we found high
accumulations of ETS, we also discovei-ed an excess of fungi
and bacteria in the HVAC system. The:ae microorganisms usually
are found to be the primary causes of the complaints and acute
adverse health effects reported by building occupants.
Dirt in Duct Systems
We have also found that HVAC systems are often
poorly designed and negligently maintained. Excessive dirt
accumulations are common in ductwork, even in hospitals.
Following the inspection of a number of buildings, hundreds of
pounds of fungi, dust, and dirt have been removed from such
ductwork. Bird, insect, and rodent carcasses and excess
amounts of dust have been found in many buildings where
employees have complained of eye irritation, headaches,
fatigue, nausea, allergies, and general respiratory problems.
Of course, since the ductwork is out of sight, it is also
invariably out of mind. Thus, it is common for the blame for
these types of problems to be laid e7.sewhere.
Energy Conservation
Indeed,.the complex of symptoms that we have
mentioned - the "sick building syndrome" - may result
primarily from energy conservation e.Eforts to seal buildings
and reduce the.infiltration/exfiltration of air. Such efforts

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have reduced the natural infiltration of fresh air that
previously-existed in many buildings, exacerbating the often
undiscovered problem of a poorly designed or maintained HVAC
system.
In addition to tightening buildings and sealing
windows, building managers have shut down air conditioning
systems at night and on weekends in an effort to lower energy
costs. When the air conditioning is shut down in humid
climates, condensation builds up and settles inside the
ductwork. If dirt is present in damp ductwork, spores and
microbes can flourish, only to be spread throughout the
building once the HVAC system is turned on the next morning.
This often results in Monday morning complaints of building
odors or building sickness that disappear during the week,
only to recur the following Monday morning. To save more
energy, automatic temperature controllers are used to cycle
fans on and off during the day. Vibrations from the start-up
of these fans can cause dirt and micrcbes trapped inside
ductwork to be dislodged and carried into occupied areas.
Another energy conservation effort that may
contribute to sick building syndrome is the recirculation of
indoor air, at the expense of fresh oL.tdoor air. This may be
the result of either a deliberate policy or shortsightedness
on the part of the designers. This re!sults in the continuous
redistribution of infectious microbes, allergenic dusts and
spores from office to office and floor to floor. Improper
ventilation can..sometimes be carried t.o extr.emes._ Typically

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we find the fresh air dampers were-closed completely-in over
35% of those buildings studied by HBI. One misgu-ided engineer-
actually had bricked up the fresh air vents to save energy.
All of these buildings were operating with 100% recycled
indoor air. The lack of an adequate fresh air supply, coupled
with dangerously low air exchange rates, has led to hazardous
ventilation conditions in many of the buildings evaluated by
HBI. Similarly, over 50% of the investigations conducted by
NIOSH from 1978-1987 attributed the indoor air quality
problems to inadequate ventilation.
Poor Air Filtration
Modern filter technology can easily cope with the
numerous particulate matter that is routinely carried in the
indoor air. Unfortunately, however, there is far too much
ignorance in this area. Frequently good filters are poorly
installed allowing air bypass, but more frequently we see a
move to cheaper, less efficient filters. Many buildings
attempt to clean the air with filters no better than butterfly
nets. Compound this with the lack of maintenance given to the
filter systems and the infrequent changes of filters and it is
hardly surprising that airborne pollLitants accumulate.
Methodology of Dealing with Indoor Pollution
Instead of a single-minded focus on specific
'pollutants, we believe very strongly in a generic engineering
approach to deal with all pol-lutants at the same-time. In our
U.S. experience of over 80 million square feet of building
studies,-the major contr-ibutors to poor air were threefold:

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(1) Poor Ventilation
Inadequate ventilation 62%
Zero fresh air intake 33%
(2) Poor Filtration
Inefficient air filters 43%
(3) Dirt in Ventilation Systems
Contaminated air handlers 36%
Contaminated ductwork 22%
We are convinced that improvirg ventilation rates,
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upgrading filters, and cleaning
up the air handling system
will eliminate over 80% of indoor pollution problems. Such
changes will improve worker productivity, enhance staff
morale, and reduce absenteeism however, many managers have
decided to ban smoking as an apparently cheap and easy way to
solve indoor air quality problems. Unfortunately, this simply
does not work.
HBI has determined that the presence of high
concentrations of tobacco smoke indicates that a much more
serious problem exists. Poor ventilation and improperly
maintained ventilation systems are the primary causes of poor
indoor air. When such conditions prevaLl, all the invisible
and odorless pollutants are also trapped. Many of these are
potentially far more dangerous than ETS.
Persistent indoor air quality complaints therefore
can be resolved only if building managers and operators are
prepared to focus on building air handling systems in an
appropriate manner. High concentrations of ETS are sumptom,
not a cause of these complaints. Its elimination can effect
no cure.

of this
CRITIQUE OF COMPENDIUM
There follows specific comments on selected chapters
compendium, either where we feel there are flaws or
misconceptions, or where we have construetive contributions to
make.
General
We feel that in many areas of this compendium the
list of papers and authors referenced to tends to be
selective; there is a broad range of research, findings
and
conclusions on this topic and we feel the compendium needs to
reflect this breadth of information. Suggestions for
additional authors are made where relevant in each chapter.
Chapter 10
This entire chapter, by its title, examines "no
smoking policies" at the work site. It is obvious, however,
that there are many options which will deal with the issue of
smoking in the workplace. In our opinion, smoking can
comfortably be tolerated in offices employing the ventilation
rates as defined in ASHRAE Standard 62- 1989.
In the event that dedicated smoking lounges are
specified, we again draw attention to RSHRAE's ventilation
rates for these areas and suggest that all such lounges should
be equipped with local area exhaust capability.
Policies For Dealing with Smoking in the Workplace
Attempts to solve a tobacco smoke problem alone
without dealing with ventilation as a whole could leave
- signif_icant =env-i=ronmental-.pr-oblems unsolved. Evidence of this

is shown in work by NIOSH and our-own published--work--which-
found 2% - 4% of bui-ldings-investigated for indoor air quality
problems respectively had ETS as their major pollutant source.
An example of a potentially misplaced smoking ban
was shown in a building owned by a majoi bank with indoor air
quality complaints recently. An occupant questionnaire
commissioned by the management resulted in a proposed smoking
ban. On investigation of the subject building, however, the
.HVAC system was found to be operating on 100% recycled air,
with the outdoor air dampers closed. Even when they were
open, the system was capable of deliver;.ng only 2 to 5 cfm
outdoor air per occupant. The filters were found to be
inefficient, and excessive fungal growths were found inside
the ductwork with correspondingly high numbers of their spores
in the air of the office area. Once ventilation, filtration,
and hygiene were improved, complaints were reduced and the
proposed smoking ban was subsequently found to be unnecessary.
Designated Smoking Areas are often a practical
political solution which balances the objectives of
non-smokers with the smokers' wishes. laith some
thoughtfulness in the selection of the smoking areas with
respect to prevailing ventilation conditions, the policy of
designating smoking areas works very satisfactorily. However,
problems with designated smoking areas have frequently been
found in indoor air quality investigations due to careless-
ness. Cafeteria areas are often designated as smoking areas
by management, despite ventilation systems there which are

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clearly-unable to cope. A fundamental p.itfall of the.desig-
nated smoking area concept, as-a.whole, is that in a large
building served by many air handling uni-=s, it concentrates
all the smokers into an area served by oaly one unit. The
capacity of this unit to dilute this more concentrated smoke
load is now often exceeded, delivering more, not less, ETS to
non-smokers also served by this unit.
If there is a requirement to establish non-smoking
areas within a building, we recommend the designation of many
small smoking areas throughout the building ensuring that no
individual air handling unit is required to cope with more
smokers than it has the capacity to handle.
Air Cleaning equipment marketed specifically for
removal of ETS components from room air is another option.
These include electrostatic precipitators, activated charcoal
filters and HEPA filter units. All three have their place in
removing respirable dust from the air. Dnly activated
charcoal systems will deal with odor, however. We have found
that all types of retrofitted air cleaning equipment
frequently are left unserviced and dirty, resulting in poor or
no air cleaning capacity. The most effective devices for
removal of perceived signs (both olfactory and visual) of ETS
appear to be a combination of good quality filters, such as
HEPA, or equivalent, followed by chemical sorption of odorous
gases with activated charcoal or other proprietary media.
"Dilution Ventilation" is another solution. This
term refers to "-dilution of contaminated air with

- uncontaminated air- in a general ar.ea,-room-, or building-, for
the purpose of health hazard or nuisance control."
Those who feel that dilution v.antilation is an
inadequate-solution to ETS exposure include Repace and Lowry.
They maintain that for adequate protection from lung cancer, a
standard of 0.75 µg/m3 RSP from ETS should be adopted in the
office workplace environment. They then calculate that this
would require as much as 5,400 cubic foot per minute per
person of fresh air brought into the building to dilute ETS
generated particulates to this level. Our data shows this
figure of 0.75 µg/m3 to be an unrealistic goal. This will be
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the case even in non-smoking offices. Since even dry outside
air might have an RSP value of between 10 and 60 µg/m3, any
attempt to attain a 0.75 µg/m3 standard when outdoor air is at
these levels is clearly impractical.
ASHRAE base their ventilation standard on achieving
control of moderate amounts of smoking. The most practical
long term solution to eliminating most ETS related problems,
along with a wide range of other commonly found indoor
pollutants, is to ventilate office buildings, whether or not
smoking is allowed, to this standard of 20 cfm per person of
outdoor air in office areas.
Finally, Exhaust Ventilation offers another workable
approach. This policy involves the designation of smoking
areas in buildings and the retrofitting of exhaust systems to
those areas. When properly installed, the
advantages to this
~ -system are clear - no -reentrainment of ETS into-the return
