NYSA TI Single-Page 4
Abstract
William S. Cain and Larry G.
Fields
- Named Organization
- American Conference of Governmental Industrial Hygienists (ACGIH)
- American Society of Heating, Refrigerating and Air Conditioning Engineers
- Archives (National Archives and Records Administration)
- ASHRAE (Am Society of Heating, Refrig and AC)American Society of Heating, Refrigeration and Air Conditioning
- City University
- Department of Commerce (DOC)
- Harvard School of Public Health
- John Wiley & Sons (Publisher)
- National Research Council
- New York Academy of Sciences
- *University of California Berkeley (use University of California at Berkeley)
- University of Connecticut
- US Department of Energy
- Named Person
- Berglund, Larry G.
- Berkeley, Lawrence
- Cain, William S. (CIAR SAB, Epidemiologist, Yale U)1988
- Chapin, Charles V.
- Doren, A. Van
- Duffee, Richard A.
- Hill, Leonard
- Hollowell, C.D. (scientist)
- Hollowell, Craig
- Horwood, Ellis
- John, G. Berglund
- Pierce, John B.
- Rosenfeld, Arthur
- Sieve, Tyler
- Simon, John
- Stahl, W. Ho
- Stevens, P. S.
- Turk, Amos
- Date Loaded
- 18 Jul 2005
- Box
- 0624
Document Images
T!05390292

LBL-9578
EEB-Vent 79-19
VENTILATION AND ODOR CONTROL: PROSPECTS FOR ENERGY EFFICIENCY
A Review of the Literature, with Reco~endations for Research
Final Report of Phase I
William S. Cain and Larry G. Berglund
John Bo Pierce Foundation Laboratory
New Haven, Connecticut
Richard A. Duffee
TRC Environmental Consultants
Weathersfield, Connecticut
Amos Turk
City University
New York City, New York
November 1979
Prepared under UCLBL P.O. No. 4622602 for the Energy Efficient
Buildings Program, Energy and Environment Division, Lawrence
Berkeley Laboratory. Principal Investigators: Craig Hollowell
and Arthur Rosenfeld.
The work described in this report was funded
by the Office of Buildings and Community Systems,
Assistant Secretary for Conservation and Solar
Applications of the U.S. Department of Energy
under contract No. W-7405-ENG-48.
T!05390293

VENTILATION AND ODOR CONTROL: PROSPECTS FOR ENERGY EFFICIENCY
A review of the literature, with recon~endations for research
William S. Cain, Principal Investigator
Larry G. Berglund
Richard A. Duffee
Amos Turk
Submitted by:
/'~ohn B. Pierce Foundation Laboratory I
290 Congress Avenue
INew Haven CT 06619
Date: November 1979
Prepared for:
Energy and Environment Division
Lawrence Berkeley Laboratory
University of California
Berkeley, CA 94720
-iii-
T105390294

CONTENTS
EXECUTIVE SUMMARY
INTRODUCTION
Odors
Odor Sources and Energy Efficiency
Energy Conservation and Ventilation Codes
Plan of the Report
INVESTIGATIONS OF VENTILATION REQUIREMENTS
New York State Commission on Ventilation
Derivation of Functional Relations
ODOR CONTROL
Deodorization of Recirculated Air by Granular Media
Activated Carbon
Other Granular Media
Alternatives to Granular Media
ODOR PERCEPTION
Nonuniformity
Nonlinearity
Interactive Phenomena
Lability
Conmon Chemical Sense
Physical Factors in Odor Perception and Ventilation
Odor Perception and Health: Some considerations
ANALYTICAL AND PSYCHOPHYSICAL MEASUREMENT
SUMMARY AND PROSPECTS
REFERENCES
7
12
24
24
25
28
30
32
32
34
36
38
40
41
46
48
53
56
oV-
Ti05390295

EXECUTIVE SUMMARY
Ventilation serves to dilute contaminants that arise in occupied spaces.
Generally, the most bothersome contaminants comprise organic chemical substances
present only in relatively small amounts. Even in small amounts, these may im-
part a definite odor to a space. Accordingly, quantitative requirements for
ventilation comprise, in effect, requirements for odor control. Because the odors of
human bodies, tobacco, smoke, cooking, and waste defy simple analysis by instrumental
means, the most direct way to decide ventilation requirements is to perform psycho-
physical experiments. These can connect the magnitude and objectionability of odor
to such variables as source and magnitude of contaminants (e.g., number of occupants,
number of cigarettes smoked per hour), rate of ventilation, temperature, humidity,
duration of occupancy, use of filter media, and various secondary variables.
The realization that requirements for mechanical ventilation rest rather di-
rectly on the need to control odors came about only gradually. Before the~l~,
mechanical ventilation requirements were generally seen to arise from the need to
control uncharacterized, but putatively toxic gases generated during occupancy.
Thereafter, particularly during the 193Os, the basis for ventilation shifted from
health effects to welfare effects. It then became clear that ventilation rates
necessary to protect welfare (to eliminate annoyance, discomfort) offered more than
enough air to protect health. Psychophysical experiments on occupancy odor, per-
formed in that era, provided the underpinnings for modern ventilation standards.
Those experiments, primarily the conception of C. P. Yaglou and associates, have
exerted more leverage than ever i.ntended. Admittedly incomplete in their time, the
experiments on ventilation requirements deserve reinspection and extension with
modern facilities and modern methods of analytical chemistry, particulate monitoring,
and psychophysical evaluation. Five broad issues of particular importance include
l) the reported need for vastly higher ventilation rates per person under crowded
than under uncrowded conditions, 2) the stability of various odorous contaminants
(e.g., tobacco smoke odor) after removal of the source, 3) the role of temperature
and humidity in the generation and perception of odorous contaminants, 4) the possi-
bility that indoor air cleaning via filtration can eliminate the need for high quan-
tities of ventilation air and can thereby save energy, and 5) whether results obtained
in an "ideal" ventilation system (i.e., an aluminum lined room with precise control
of environmental variables and air delivery) will generalize to field situations.
These, and various associated issues (e.g., the contribution of particulate matter
to tobacco smoke odor, the difference in odor tolerance between an occupant in a room
and a visitor to a room), form the basis for newly begun laboratory and field experi-
ments on ventilation and odor control, with particular emphasis on the quest for
energy efficiency in ventilation.
-vii-
TI05390296

INTRODUCTION
The indoor air generally contains a great variety of substances, organic
and inorganic, present only in low concentrations. In a well-designed and
well-tended building, these substances often exist at levels low enough to lack
discernible impact on occupants. At levels high enough to have adverse impact,
the substances are viewed as contaminants.
A contaminant may act upon such biological targets as the airways, the
liver, the central nervous system, and so on. Some contaminants may cause an
immediate reaction, others a much delayed or a cumulative reaction. Some may
pose little hazard when inhaled alone, but an amplified hazard when inhaled
along with other contaminants. Some may have little impact on the majority of
persons but a large impact on a sensitive minority.
Generous ventilation has provided the traditional means to combat accumulation
of indoor contaminants. Nevertheless, the cost of ventilation, on the average more
than one-quarter of the operating cost of a building, increases proportionally with
the cost of energy and therefore provides considerable incentive to search for
energy efficiency. The present report will deal primarily with technical features
of ventilation and the control of odorous contaminants. It will pursue a dual goal:
to maintain acceptable air quality indoors and to achieve energy efficiency in the
maintenance of air quality.
Odors
In addition to any ability to cause adverse impact, most airborne organic
substances possess the con~non ability to excite olfaction (1). Many become
detectable by smell at concentrations well below one part-per-million (ppm).
Indeed, some evoke strong, even overpowering odors at concentrations in the
ppm range.
Like other sense modalities the sense of smell behaves as an adaptive
channel of information. For instance, olfaction manages to block the ingestion
of various unhealthful substances (e,g., spoiled meat} that might be deemed
acceptable by taste. When used to evaluate the properties of substances taken
into the mouth, olfaction serves as a "contact" sense in a manner similar to
taste. Olfaction also serves as a "distance" sense, a channel for information
about objects outside the body. When using the modality in this way, a person
can readily succumb to the temptation to ascribe to the odorous air charac-
teristics more properly attributed to the source of odorant. Hence, foul smell-
ing air can seem dangerous in itself rather than merely a signal of the pre-
sence of unsanitary conditions. A passage regarding the views of the eminent
public health physician Charles V. Chapin illustrates a common-confusion (2):
Probably the most conspicuous aspect of the sanitary environment
of Providence (as of other cities) in 1884 was the stench. It
had odors from its hundreds of stables, its polluted streams,
its dead dogs or horses, and its thousands of foul privy vaults
and cesspools. When the odors became so intense that even the
people who lived among them were nauseated, it is no wonder that
many persons associated diseases with bad smells. And when disease
did come out of certain kinds of foul smelling dirt, it was only
logical for people to fear and wish to eliminate filth ... Chapin
did not fear odors as such. He was one of a few in America before
1885 who followed the English sanitarian John Simon in pointing
out that the danger from filth was not in the stench but in
specific disease germs. [p. 45]
T105390297

In the late 19th century when physiologists began to experiment in earnest on
the biological basis for ventilation, the question of acceptable odor levels
indoors also attained prominence. Various scientists of the time considered
the organic substances given off by human bodies as particularly harmful, even
lethal (3):
Organic matter is given off from the lungs and skin, of which
neither the exact amount nor the composition has been hitherto
ascertained. The quantity is very small, but of its importance
there can be no doubt ... Since this organic matter has been
proved to be highly poisonous, even apart from carbon dioxide
and vapor, we may safely infer that much of the mischief re-
sulting from the inspiration of rebreathed air is due to the
special poisons exhaled by the body.
Absence of techniques to detect small amounts of organic vapors meant re-
liance on the nose as an indicator of safety. Since that era, it has become
clear that body odor in particular carries little hazard. Nevertheless, through-
out this time odors have never ceased to play a strong role in the determination
of ventilation requirements. Whether for reasons of health or esthetics, odors
will continue to figure in ventilation practice. Therefore, any effort to
discover ways to conserve energy in ventilation must confront the issue of how
odors arise, how they are perceived, and how to control them.
Odor Sources and Energy Efficiency
Odors may arise from almost any indoor activity. Tobacco smoke forms a par-
ticularly notorious odor nuisance. Its persistence and its change in character
over time (i.e., from fresh, but irritating, to stale and sour) account for much
of its notoriety. Places of habitual smoking may never lose their odor even when
ventilated continuously at very high levels. The cost of such high rates of ven-
tilation gives incentive to displace or eliminate the source. Where possible,
elimination of a source of odor provides the most economical and energy efficient
means of control. Odor problems in the workplace, for instance, often arise from
poor "housekeeping." The same can hold true in residences and in commercial and
institutional buildings. Such housekeeping chores may include, among other things,
cleaning of ducts and cooling coils and removal of. filters in a ventilation system.
This kind of housekeeping acknowledges that the system may become a secondary source
of odor from dust, bacteria, mold, spores, and adsorbed organic materials.
I.n many instances, odors arise from sources (e.g., kitchen stoves, toilets)
that allow some control of the source, but not complete removal. The most energy
efficient means to cope with such high intensity sources may include local exhaust
with perhaps some recirculation of the exhaust air. In general, however, odor con-
trol will derive from the need to cope with such things as effluvia from bodies,
emanations from building materials, and ongoing activities of occupants (e.g.,
eating, drinking). These matters require general ventilation and pose the energy
relevant issue of whether a space should continuously'receive the amount of vent ]a-
tion air dictated by the so-called design occupancy. Many spaces are commonly occu-
pied at much lower levels. The matter of ventilation on demand, achievable through
monitoring and control of concentrations of carbon dioxide, oxygen, carbon monoxide,
or other, as yet, unspecified contaminants,will receive little direct attention here.
Nevertheless, this manner of gaining control over the atmospheric environment in a
building is potentially compatible with both high indoor air quality and low expen-
diture of energy.
2
T!05390298

Energy Conservation and Ventilation Codes
The present report will give primary consideration to odors, but will neces-
sarily pay some attention to the thermal attribute of the indoor environment.
These factors play companion roles. Ventilation can serve simultaneously to
bring the indoor environment under thermal control, e.g., using outdoor air to
cool a warm space, as well as to dilute chemical contaminants. Furthermore,
occupants may confuse thermal and chemical attributes perceptually, viz., may
decide that stuffiness arises from poor air quality as opposed to overly warm
air. The intimate relationship between these factors takes on particular impor-
tance in efforts to conserve energy. Any reduction in the amount of ventilation
air normally necessary to control odors will reduce the energy consumed to heat,
cool, humidify, or dehumidify that air. Such savings can add to those achieved
through lowering the settings of thermostats in winter and raising the settings
in summer.
Within the last few years it has become common for jurisdictions to adopt
model building codes. The codes include those of l) the Building Officials and
Codes Administrators International (BOCA), used mainly in the midwest and north-
east, 2) the International Conference of Building Officials (ICBO), used mainly
in the west, and 3) the Southern Building Code Congress International (SBCCI)
used mainly in the south and southeast. In some instances, a particular model
code governs building practices in all local jurisdictions within a state. In
other instances, local officials will have the opportunity to choose between the
state code or a specified model code. In some states (e.g., Texas), one model
code will prevail in one area and another model code in another area. Irrespec-
tive of such seeming complications,the country has in fact begun to converge
upon uniformity in building codes and accordingly in ventilation codes.
In a particularly strong gesture toward uniformity, the three model code
groups (BOCA, ICBO, SBCCI) worked together with the National Conference of.
States on Building Codes and Standards (NCSBCS) to draw up an energy conservation
code (The Code for Enerqy Conservation in New Buil.dinB Construction). This code,
in actuality a section of a total code, has already become or wil'l become part
of the BOCA, ICBO, and SBCCI model codes. The code for energy conservation finds
its parentage in Standard 90-75 (Energy Conservation in New Buildinq Design) of
the American Society of Heating, Refrigerating, and Air-Conditioning Engineers.
Table l shows that virtually all large jurisdictions have already or will soon
conform to energy conservation standards through adherence to one or another
model code or through the adoption of a separate state code rooted in a model code
or ASHRAE Standard 90-75. Indeed, only five jurisdictions fail at present to show
overt action toward the adoption of an energy-efficient code. The information in
Table l was gathered by NCSBCS and disseminated on May 25, 1979.
The ventilation component of the energy conservation model code derives
from ASHRAE Standard 62-73, Standards for Natural and Mechanical Ventilation~
That standard lists ventilation requirements per occupant for a great variety
of residential, commercial, industrial, agricultural, and institutional spaces.
The standard specifies, space by space, two requirements: minimum and recom-
mended. The recommended requirements actually form an interval, e.g., ]5-20
cfm (7.5 - lO L/s) per occupant. Minimum requirements fall on the average
30% below the midpoint of the recommended range. Table 2 gives examples for
a few spaces.
*Standard 62-73 is currently under revision.
appear in 1980.
3
A revised standard will probably
T105390299

Jurisdiction
Table l
NCSBCS Survey of Energy Conservation Codes
Energy Conservation
Code
Jdrisdiction
Energy Conservation
Code
Alabama SBCCI Nebraska (ICBO)
Alaska (ASHRAE 90-75) Nevada MCEC
Arizona (State Code)* New Hampshire MCEC
Arkansas (State Code)* New Jersey BOCA
California State Code New Mexico ICBO
Colorado MCEC New York State Code*
Connecticut State Code* North Carolina State Code
Delaware (MCEC) North Dakota ICBO
District of Ohio MCEC
Columbia (City Code) Oklahoma None
Florida State Code*
Oregon ICBO
Georgia MCEC Pennsylvania (ASHRAE 90-75)
Hawaii ICBO Rhode Island ASHRAE 90-75
Idaho ICBO South Carolina SBCCI
Illinois (State Code)* South Dakota (MCEC)
Indiana MCEC Tennessee MCEC
Iowa MCEC Texas (MCEC)
Kansas State Code
Utah MCEC
Kentucky MCEC Vermont (ASHRAE 90-75)
Louisiana (MCEC) Virginia BOCA
Maryland (ASHRAE 90-75) ASHRAE 90-75
Massachusetts MCEC Washington State Code
Maine (State Code) West Virginia None
Michigan ASHRAE 90-75 Wisconsin State Code*
Minnesota ASHRAE 90-75 Wyoming ICBO
Mississippi (MCEC) American Samoa MCEC
Missouri (MCEC) Guam ICBO.
Montana MCEC Puerto Rico MCEC
Key:
( ) Denotes Legislation Pending
ASHRAE 90-75 ASHRAE STANDARD 90-75
BOCA Model Code, Building Officials & Code Administrators Inter-
national, Inc.
ICBO Model Code, International Conference of Building Officials
MCEC Model Code for Energy Conservation in New Building Construction
SBCCI Model Code, Southern Building Code Congress International,lnc.
Asterisk(*) denotes obvious incorporation of energy conserving aspects of a
model code or ASHRAE 90-75. Codes or pending codes for California, Maine,
and North Carolina also include some such aspects.
4
Ti05390300

Table 2
Examples of Ventilation Requirements Per Occupant
Recommended in ASHRAE Standard 62-73.
Residential bedrooms
Conference rooms (small)
Public rest rooms
Classrooms
School libraries
Minimum Recomended
5 cfm (2.5 L/s) 7-10 cfm (3.5-5 L/s)
20 (I0) 25-30 (12.5-15)
15 (7.5) 20-25 (I0-12,5)
10 (5) ]0-15 (5-7.5)
7 (3.5) I0-12 (5-6)
ASHRAE Standard 90-75 on energy conservation specifies use of the minimum
values from Standard 62-73. This means that new buildings should now deliver ap-
proximately 70% of the outdoor air delivered prior to the energy conservation
standard. These new recommendations have considerable impact because they form
the ventilation recommendations of the Code for Energy Conservation in New Building
Construction jointly prepared by BOCA, ICBO, NCSBCS, and SBCCI. In essence, then,
the various code-bodies of the United States have shown a strong desire to achieve
both uniformity and energy efficiency in ventilation.
ASHRAE's assessment of ventilation requirements arises mainly from consensus
regarding the outdoor air necessary to maintain indoor comfort. As will become
evident below, the minimum requirements bear similarity to the outcome of laboratory
research on the acceptability of odors generated during occupancy.
Plan of the Report
The remainder of this report will highlight the various factors that play a
role in the determination of ventilation requirements for odor control. First, the
report will review studies that uncovered and quantified the connection between
odors and ventilation requirements. Although motivated by an interest in public
health and hygiene, such studies were generally reported in the engineering litera-
ture. Not surprisingly, therefore, most hygienists and public health specialists
have traditionally paid little attention to chemical contaminants in the residential,
commercial, and institutional environments. The presumed adequacy of ventilation
has allowed such professionals to focus on chemical contaminants in the workplace
and in the ambient air. Recent discoveries regarding excessive levels of formalde-
hyde in buildings lined with chipboard (4), excessive levels of particulate matter
in the vicinity of smokers (5), and excessive levels of oxides of nitrogen in homes
with gas stoves (6), have, in conjunction with the need for energy efficiency, re-
focused attention on the origin and adequacy of nonindustrial ventilation rates.
Subsequent to a review of the research basis for modern ventilation rates, the
varieties of odor control applicable indoors will receive attention. The section
on control will deal at length with chemical and engineering considerations in the
use of granular filter media, the most practical means of indoor odor control. In
the present context, the term odor control refers to the elimination of small amounts
of gaseous materials. Some such materials happen to evoke odor and provide no other
incentive for control. Nevertheless, the control procedures will eliminate many
T105390301
