Congress of the United States
House of Representatives
Washington, DC 20515-4607
THE TESTIMONY OF GRAY ROBERTSON PRESIDENT OF HEALTHY BUILDINGS INTERNATIONAL INC. BEFORE THE SUBCOMMITTEE ON HEALTH AND THE ENVIRONMENT COMMITTEE ON ENERGY AND COMMERCE U.S. HOUSE OF REPRESENTATIVES
MARCH 17, 1994
Introduction
I am the President of Healthy Buildings International Inc., a company that specializes in the
study and assessment of indoor air quality. Since we incorporated in 1981, we have studied
approximately 1,000 major buildings throughout the world. We serve our clients from five offices
in England, Australia, Spain, Canada and our headquarters office located in Fairfax, Virginia.
For 13 years our activities on behalf of our clients have been devoted to the study of indoor
air problems. We analyze the air for fibers of textiles, asbestos, glass and mineral wools, radon,
carbon monoxide, exhaust fumes, pesticides, detergents, carpet and furniture emissions, PCBs,
volatile organic chemicals, bacteria, fungi and, of course, tobacco smoke. An integral part of
our investigations is the study of the ventilation systems, their design, control sequences and
operational policies. These experiences are all dedicated to cleaning up the indoor environment,
which makes our testimony especially relevant to any debate on these issues.
Major corporations such as IBM, GTE, Digital Equipment, Union Carbide, Pepsi Cola plus
government agencies including the US Department of Health and Human Services, the Social
Security Administration, Housing and Urban Development, the Federal Reserve Bank and the
United Nations have all retained our services to accomplish the goal of clean indoor air. These
references plus over 300 other corporate clients confirm our qualifications as experts in this field.
Some of our clients have chosen to ban smoking. A number of others prefer the practice of
restricted smoking areas whereas others continue with discretionary smoking. Three different
philosophies yet all have expressed satisfaction with their indoor air quality programs and the
resulting quality of their indoor air. How and why? Because all adopted our primary
recommendations of maximizing the capacity of their ventilation systems, of improving where
necessary their filtration standards and all, because of our encouragement, have paid greater
attention to correct operating practices concerning their ventilation control equipment.
My testimony today is divided into two parts. Part One concerns the techniques we use to
manage smoke in the indoor environment. Part Two looks at the economic impact of HR-3434.
Part One -- The Client-HBI Interface
Some clients have called us in to resolve complaints about tobacco smoke. Others have had
absentee problems. Most were concerned with worker productivity. An ever increasing number
of clients feared possible litigation. Now we are seeing an added influx of enquiries as a result
of the Environmental Protection Agency's (EPA) risk assessment concerning environmental
tobacco smoke.
Our advice to all our clients is not to lose sight of the long term objective -- a comfortable and
productive workplace with reductions in the concentration of all pollutants, including smoke.
Fortunately, smoke, from the perspective of a ventilation engineer, is a relatively easy component
of the indoor air to manage. Microbes, with their incredible capacity to reproduce, coupled to their
ability to lie dormant over long periods, are much harder to control. Furthermore, for every
building where we have encountered tobacco smoke problems we have experienced tenfold that
number of buildings with microbial contamination. These organisms positively cause allergies,
certainly can cause infections and indisputably the secreted toxins from some are identified as
potent carcinogens. Neither we, nor you, can afford to dismiss any indoor pollutants be they
microbes, dusts, fibers or chemicals.
Carcinogens in the Workplace
Less than 40 percent of the 700 USA buildings that we have studied, allow smoking and this
number is dropping. However, we can categorically state that the air in 100 percent of them
contain substances considered by the EPA to be known or probable human carcinogens. Indeed,
no less than 95 percent have been found by us to contain the class A carcinogen benzene.
Others, including asbestos, radon, chloroform, trichloroethylene, carbon tetrachloride and styrene,
are found throughout the buildings we study. These are present regardless of whether smoking
is allowed or banned.
Without being too melancholic, perhaps I can remind you that substances thought to be
carcinogens are also widespread in the food chain. Mushrooms, nuts, corn, spinach, beets,
lettuce, fish and shellfish, oranges, peppers and numerous herbs and spices contain naturally
occurring chemicals that have been classed as carcinogens.
Returning to the implications of the EPA's statement. First let us recognize that the EPA has
no statutory authority to regulate indoor air quality. The authorized agency is the Occupational
Safety and Health Administration (OSHA). This agency is currently at the formative stage of
developing rules on indoor air quality, including tobacco smoke.
OSHA has for many years been charged with the responsibility of protecting workers from
exposure to many chemicals including those thought to be carcinogens. They accomplish this
by ensuring that airborne concentrations of carcinogens such as benzene, arsenic, asbestos,
cadmium, etc., are maintained below so-called Permissible Exposure Levels (PELs). These are
usually eight hour time-weighted averages. Also, the National Institute for Occupational Safety
and Health (NIOSH) publishes Recommended Exposure Limits (RELs). Perhaps of more
relevance, however, are the Threshold Limit Values (TLVs). Interestingly, these TLVs are
specifically set to protect worker health. Furthermore, the source of many of these TLVs, the
American Conference of Gpvernmental Industrial Hygienists, state that TLVs refer to airborne
concentrations of substances below which it is believed that nearly all workers may be repeatedly
exposed, day after day, without adverse health affects. There is as yet no TLV for tobacco
smoke.
The Role of Ventilation
With respect to smoking, in the absence of a TLV, we advise prudence such that managers
minimize non-smoker exposure to tobacco smoke in commercially viable ways. Certainly we
stress the need for good ventilation and filtration practices whether or not smoking is allowed.
Indeed, a prerequisite of any workplace that wishes to provide a comfortable and productive
environment for its staff is to first ensure that generally accepted ventilation rates prevail.
Specifically, for offices, restaurants, hotels, bars, etc., the ventilation rates should comply with the
American Society of Heating, Refrigerating and Air Conditioning Engineers (ASHRAE) Standard
62-1989 "Ventilation for Acceptable Indoor Air Quality." In the case of offices, ASHRAE stipulates
a minimum outside air ventilation rate of 20 cfm/person. This ASHRAE standard allows for a
moderate amount of smoking and, when properly adopted, complaints are unusual.
Furthermore, the committee members responsible for the specification of ASHRAE 62-89
ventilation rates did not simply choose a random number for ventilation in areas of moderate
smoking. Rather, their value was based on specific studies which showed 80 percent visitor
acceptance at 15 cfm per person of ventilation air, with 1.1 cigarettes per hour per smoker with
one-third of the population smoking (Jansen J.E., "Ventilation for Acceptable Indoor Air Quality",
ASHRAE Journal, Oct. 1989, pp. 40-48). The use of 20 cfm of outdoor air per person for offices
provides an adequate margin of comfort.
Smoking Areas
If after improving the air handling characteristics of an office building, additional actions are
considered necessary, it is not unreasonable to separate smoking and non-smoking areas or to
designate areas for smoking. However, it is important that such designated areas be correctly
ventilated.
The smoking lounges can be designed with their own dedicated air supply and exhaust
system. Or, as suggested by ASHRAE, they can be incorporated into buildings using the air
supplied by the existing ventilation system. The air to the smoking lounge can be either ducted
supply air or it can be "transfer air" -- i.e., air deliberately induced into the lounge from adjoining
areas. So long as the designated smoking areas or its dedicated smoking lounge is maintained
at a negative pressure relative to adjacent areas, the laws of physics preclude any migration of
smoke from the lounge to nearby areas.
Such designs are commonly practiced in many buildings. In our experience in studying
hundreds of buildings, we have found nonsmokers and smokers perfectly happy with such an
arrangement.
Bars and Restaurants
In the case of existing restaurants, bars, bowling alleys, etc., it is not always practical to
designate specific smoking areas; nor, fortunately, is it necessary. Spatial separation, even
without physical barriers, can be very effective in minimizing non-smoker exposure to ETS.
Indeed, proper engineering of the ventilation systems, including the provision of correct air flows,
can obviate the need for physical barriers between smoking and non-smoking areas. It is a fact
of basic physics that water cannot flow up a hill. Similarly, air cannot move against a pressure
gradient. If the smokers are positioned adjacent to the exhaust system of a room and the
non-smokers are placed near to the supply, the air movement is inevitably from the supply grilles
to the non-smoking area then on to the smoking area and from there directly to exhaust.
Providing that the supply and exhaust systems are sized correctly, the smoking area will always
be operating at a lower pressure than the non-smoking one, so no smoke can drift toward the
non-smokers.
Proof of the efficacy of such separation has been demonstrated by others. For example, two
recent papers (1,2) report no detectable components of ETS even in air recirculated through
HVAC systems from smoking areas. The first was funded by the cigarette and tobacco surtax
fund of the State of California and the second was funded by the US Public Health Service
Region III.
Part Two -- Economic Impact of HR-3434
In the role of a businessman with a knowledge of the property management and building
services industry, it would be remiss of me if I did not comment upon some of the information you
have received from others, including the EPA. Specifically, Carol Browner, Administrator of the
EPA, testified before this subcommittee on February 7th about the housekeeping and
maintenance cost of buildings. Her testimony included the following statement:
"In addition, a substantial potential savings in housekeeping and manintenance expenses
of buildings seems to be possible (as a result of a smoking ban) and could be in the $5 to $10
billion range".
The phrases "seems to be possible" and "could be" were perhaps included to preserve
"plausible deniability." The fact is that savings of this magnitude in housekeeping and
maintenance costs are more figments of the imagination than hard data. Is this obvious
hyperbole simply delivered to garner support or media attention?
Why are the savings impossible? To answer this, let us review the data used by the EPA.
Housekeeping and maintenance costs were based on assuming standard times to complete
specific tasks in a hypothetical 1,000 square foot unit of building. An estimate was made of the
frequency of repeating such tasks. Presumptions were made such as smoking areas needing to
have their carpets vacuumed 46 percent more frequently than non-smoking areas or furniture in
smoking areas needing to be dusted once every three days compared with once every five days
in non-smoking areas.
Using these theoretical assumptions and the assumed standard times, comparative costs
between housekeeping in smoking areas and non-smoking areas were determined. Similar
calculations based on presumptions and theoretical cost savings indicated that maintenance costs
in non-smoking areas could save $122 per 1,000 square feet. To arrive at this figure, it was
assumed that building owners would repaint smoking areas every six years and non-smoking
areas could last 12 years!
Once having arrived at potential savings of $105 in housekeeping and $122 in maintenance
costs per 1,000 square feet, the EPA multiplied these savings by 61 billion square feet to theorize
the overall impact on the nation. They concluded that national savings would be:
| Task | Theoretical Savings | Minimum Savings | Maximum Savings |
| Housekeeping | $6,375,000,000 | $3,679,000,000 | $4,906,000,000 |
| Maintenance | $7,413,000,000 | $4,278,000,000 | $5,704,000,000 |
| Total Savings | $13,788,000,000 | $7,967,000,000 | $10,610,000,000 |
Reasonableness of these Figures
Note that of the $8 billion "minimum savings" projected by EPA, 31 percent is attributed to
eliminating the need to clean ashtrays and 54 percent is attributable to reduced painting costs.
Can anyone really believe that by simply eliminating the emptying of ashtrays we could save
over $2.4 billion of cleaning costs? Is it possible, that by eliminating smoking we can reduce
painting costs by over $4 billion per year?
These sorts of calculations are a typical example of back-room voodoo economics by persons
far removed from the true facts of building service costs. I personally have discussed these
issues with senior management of two major office cleaning companies. Some of the facts that
emerged from those discussions are of relevance here.
The cleaning costs for government buildings from 1986 to 1993 have climbed from less than
$1.0 per square foot to $1.4 per square foot (Source BOMA statistics and/or Black's Guide). In
the same period we have seen a steady increase in non-smoking areas until we reach today's
status in most government buildings where smoking is totally banned or severely restricted. Why
were the cost savings for eliminating smoking not reflected in these figures? For comparative
purposes, the average cleaning cost of commercial buildings in the USA through 1991/92,
according to BOMA, is $1.08 per square foot.
The EPA's estimated cost for emptying ashtrays at $70 per 1,000 square feet represents
$0.07 per square foot. Similarly, the housekeeping savings were $105 per 1,000 square feet or
$0.11 per square foot. When I asked the cleaning companies if due to the elimination of smoking
I could expect a reduction in cleaning costs of between 7 and 11 cents per square foot they
thought I was crazy.
They point out that a typical analysis of their overall cleaning budget of $1.08 per square foot
would be: Labor 70 cents, insurance and taxes 11 cents and profits at 5 cents, total $1.08.
Furthermore, they point out that most of the buildings they now clean already practice restricted
smoking policies. Politely, they point out that they could not pass on any significant savings
whatsoever.
The savings in painting costs are also a myth. To appreciate this consider the following:
- The common areas of all major office buildings are on average, completely refurbished,
including painting and re-carpeting, every four years, whether or not smoking is allowed.
- The average office lease in the USA is approximately 5 years. Thus each 5 years the
offices are routinely painted, regardless of smoking policies. Larger corporations, negotiating
longer leases, usually also negotiate repainting schedules schedules with the owners, or elect to
cover the costs themselves. Most paint more frequently, not less frequently, than the building
owners' schedules.
- The other theoretical savings can also be shown to be figments of the imagination.
Discussions with building owners or their cleaning companies revealed that:
- Venetian blinds are rarely cleaned more than once a year.
- Frequency of vacuuming carpets is dictated by traffic patterns, not smoking policies.
- With 13 years of experience of studying buildings we have never observed smoking policy
decisions impact on the need to revise air filter replacement schedules.
- Possible Expenses Incurred by Total Smoking Bans
Lost Productivity
A building of 100,000 square feet could typically house 600 staff allowing 167 square feet per
person. Assuming these staff work 8 hours per day they collectively work 4,800 hours/day.
If 25% are smokers (150 staff), who take an average of 4 smoke breaks per day of 10
minutes duration (to leave the building, smoke a cigarette, and return to their office) then we have
150 staff x 10 mins x 4 breaks per day = 6,000 mins = 100 hours per day spent unproductively.
100 hours lost production represents 2% of the total available.
Assuming that the average worker cost $30,000 per annum in salary plus payroll associated
costs the annual payroll would be, 600 staff x $30,000 = $18 Million per each 100,000 square
feet.
2% productivity losses per 100,000 square feet = $360,000.
If we then used the EPA multiplier of 61 Billion sq ft couldn't we now expect to lose
| 61 Billion sq. ft. x | $360,000 = | $219 Billion ? |
|---|
| ----------------------- | | |
| 100,000 | | |
Energy Costs
- Elevator Costs. If we return to our model building of 100,000 sq. ft. and assume that it is
sub-divided into say 10 floors and further assume that the ground floor is a typical retail area,
then the 150 smokers (25% of staff) would need to make 600 round trips, i.e., 1,200 extra
elevator trips if they leave the building for 4 smoke breaks per day.
- Would an EPA researcher like to project how many multi-story buildings are present in 61
Billion sq. ft. of property to project total energy consumption expended by these smokers forced
outside the building?
- Door Openings. Normally an air-conditioned building operates with an interior pressure
slightly greater than the outdoor air -- on average we expect a pressure differential of 0.02" from
inside to out. Every entry or exit through the doors involves a loss of conditioned air.
In theory, each door opening of say 4' x 7' (28 square feet) could lose nearly 10,000 cfm
per minute if the pressure differential is 0.02".
Since our 150 smokers per 100,000 square feet of building take a total of 600 smoke
breaks per day = 1,200 door openings of say 5 seconds duration each, wouldn't we be justified
in working up some energy losses based on 1,200 door openings x 5 seconds each = 100
minutes at 10,000 cfm per minute multiplied by some major fraction of 61 Billion square feet?
I am not suggesting we waste time on such interesting mathematics. The fact is that there
are very tangible losses in productivity and energy related losses associated with a total smoking
ban once we assume that a significant percentage of those smokers affected do indeed leave the
building to smoke. Furthermore, once productivity losses are included in the equation these losses
dwarf the theoretical gains claimed from reduced cleaning and /or maintenance costs.
Ladies and gentlemen, thank you for giving me a hearing today. What I have described is
a small part of one of many presentations that our company makes for such recognized
associations as the American Institute of Architects, ASHRAE, the Association of Energy
Managers, the Gas Council, the Air Balance Council, the Building Owners and Managers
Association and numerous Fortune 500 corporations. Without exception these groups compliment
us on sharing the results of a decade of our research in this way. If, however, the tobacco
industry asked us to make an identical presentation we are likely to be branded as apologists for
that industry. We are not. We are an independent company with considerable expertise acquired
over 13 years of studying buildings for a very diverse client base. Today I appear before you at
the request and expense of the Tobacco Institute. However, I assure you that my findings,
statements and recommendations are based on our own independent research. Indeed I
challenge anyone to debate these issues with me and for anyone to point out where my
statements depart from well accepted engineering principles and basic common-sense.
[signed]
Gray Robertson
March 17, 1994
Healthy Buildings International Inc.
10378 Democracy Lane
Fairfax, VA 22030
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