Philip Morris
Guide to Indoor Air Pollutants Second Edition 920000
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GUIDE
TO
INDOOR AIR POLLUTANTS
Second Edition
1992
Detail Associates, Inc.
300 Grand Avenue
Englewood, NJ 07631

Key to Abbreviations
ACGIH - American Conference of Governmental
Industrial Hygienists
AF - atomic formula
ASHRAE -American Society of Heating,
Refrigerating and Air Conditioning
Engineers
AW - atomic weight
bp - boiling point
BRI - building related illnesses
C - temperature in degree centigrade
CAS - Chemical Abstracts Service
cc - cubic centimeter
CL - ceiling concentration
conc - concentration, concentrated
CPSC - U.S. Consumer Product Safety
Commission
cu m - cubic meter
DOT - U.S. Department of Transportation
EPA - U.S. Environmental Protection Agency
F - temperature in Fahrenheit
fp - freezing point
H, hr - hour(s)
IARC - International Agency for Research on
Cancer
kg - kilogram
LC50 - lethal concentration 50 percent kill
LCLo - lowest published lethal concentration
LD50 - lethal dose 50 percent kill
LDLo - lowest published lethal dose
MF - molecular formula
ml - millimeter
mp - melting point
MW - molecular weight
ng - nanogram
NIOSH - National Institute of Occupational Safety
and Health
NTP - National Toxicology Program
OSHA - Occupational Safety and Health
Administration
PCBs - polychlorinated biphenyls
PEL - permissible exposure level
ppb - parts per billion (v/v)
pph - parts per hundred (v/v) (percent)
ppm - parts per million (v/v)
ppt - parts per trillion (v/v)
RCRA - Resource Conservation and Recovery
Act
REL - Recommended Limit Value
RTECS - Registry of Toxic Effects of Chemical
Substances .
SARA - Superfund Amendments and
Reauthorization Act
SBS - sick building syndrome
STEL - short term exposure limit
TC - toxic concentration
TCLo - lowest published toxic dose
TLV -Threshold Limit Value
TWA - time-weighted average
ug - microgram
uL - microliter
WHO - World Health Organization

Table of Contents
Chapter I Introduction
.............................................................................................. 4
1. Background
....................................................................................................
................................... 4
2. Reasons to be Concerned about Indoor Air Quality
.......................:................................................ 4
3. Definitions
....................................................................................................
...................................... 5
4. Objectives of This Publication
....................................................................................................
....... 5
Chapter 11 Indoor Air Pollution in Residential Houses .......................................... 6
1. Sources of Indoor Air Pollutants
....................................................................................................
... 6
2. Contamination from Outside Sources
.......................................................................................... ... 6
3. Ventilation
....................................................................................................
...................................... 6
4. Air Exchanges
....................................................................................................
................................ 7
5. Assessing Indoor Air Quality in Homes
............................................................................................ 7
6. Ways of Improving Your Indoor Air Quality
.....................................:............................................... 8
Chapter III Indoor Air Pollution in Office Buildings ...............................................
9
1. Background
....................................................................................................
.................................... 9
2. Sources of Indoor Air Pollution
....................................................................................................
.... 10
3. Ventilation Systems
....................................................................................................
...................... 11
4. Office Equipment as a Source of Indoor Air Pollution
.................................................................... 11
5. Evaluating Indoor Air Quality in Offices
............................................................................................12
5. Resolving Air Quality Problems in Office Buildings
........................................................................ 13
6. Control Process of Indoor Air Pollution in Buildings
...................................................................... 13
7. Professional Help
....................................................................................................
......................... 14
Chapter IV Evaluation Criteria for Indoor Air Quality ......................................... 16
1. Public Health Standards
....................................................................................................
.............. 16
2. Occupational Health Standards
....................................................................................................
.. 17
3. Evaluation of Existing Standards and Guidelines
........................................................................... 17
Chapter V Common Indoor Air Quality Measurements ......................................... 18
1. Common Sampling Devices
....................................................................................................
....... 18
2. Measurement of Air Flow and Outdoor Air Quantitities
................................................................. 18
3. Air Contaminant Concentrations
....................................................................................................
19
Chapter VI Common Indoor Air Pollutants ...........................................................
21
1. List of Common Indoor Air Pollutants
............................................................................................. 21
2. Biological Hazards
....................................................................................................
....................... 24
3. Common Indoor Air Pollutants
....................................................................................................
.... 36
Chapter VI Protocols For Indoor Air Quality Investigations ............................ 199
a
I
1. Methodology
....................................................................................................
...............................
2. Background Assessment
............................................................................
. 199
199 N
~
.
.................................
3. Initial Site Assessment
....................................................................................................
...
199 i
~
.
............
4. Closing Conference
....................................................................................................
....................
5. Additional Site Assessments
....................................................................................................
...... 200
201 CA
CA
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Guide to Indoor Air Pollutants
Chapter VII Indoor Air Quality Program of Detail Associates, 1nc . .................... 203
Chapter Vill Recommended Sources of Information ......................................... 205
Appendix I References
....................................................................................... 209
Appendix 11 Indoor Air Quality Qestionnaire ......................................................
211
Index to Indoor Air Pollutants
................................................................................ 213

Guide to Indoor Air Pollutants
Chapter I Introduction
1. Background
ln the past two decades, a growing body of scientific evidence has indicated that the air within
homes,
offices and other buildings has become seriously polluted and can often be even more polluted than
the outdoor air of the largest and most industrialized cities.
In 1970, when the Clean Air Act was passed to address the problems of urbanization, industrial
development and the increasing use of automobiles, the Act was interpreted as applying only to the
air
external to structures. Most Federal programs concerned with reducing exposure in enclosed spaces
have singled out only a handful of individual pollutants for action or control under various Federal
Statutes.
In the early 1970's, formaldehyde was identified by the Consumer Product Safety Commission as the
source of acute irritant reactions and a cancer hazard. Federal programs to address another major
in-
door air pollutant - asbestos - have been in operation for some time and two major laws have been
enacted by Congress to provide loans and grants to schools with severe asbestos hazards and finan-
cial need, and to provide a regulatory framework for asbestos control in schools. In the late 1970's
and early 1980's, concern over naturally occurring radon began to rise and in 1984, when extremely
high levels of radon were discovered in homes in the Reading Prong geological formation in Pennsyl-
vania, New Jersey, and New York, radon became a major indoor air pollution Federal program.
In the early 1980's, however, research by EPA and other Federal agencies began to demonstrate that
for many pollutants, indoor levels were often higher than outdoor levels. This, coupled with the ex-
tremely high percentage of time spent indoors, gave rise to increased concern that indoor air
pollution
may pose higher health risks to the population than previously thought.
In 1986, Congress enacted Title IV of the Superfund Amendments and Reauthorization Act (SARA) to
establish an effective research effort aimed at characterizing the extent of the indoor air
pollution prob-
lem and to begin to take steps to enhance the quality of indoor air.
However, to date, no comprehensive legislation to address many of the issues raised by indoor air
pol-
lution has been enacted.
2. Reasons to be Concerned about Indoor Air Quality
Recent research shows that people spend approximately 75-90 percent of their time indoors. Some
reasons for concern include: (1) for most people, the health risks posed by indoor air pollution may
be
greater than that posed by outdoor air; (2) some groups of people who are most vulnerable to the ad-
verse effects of indoor air pollution including the elderly, the young, and the chronically ill are
exposed
to such pollution the most; (3) unlike other risks, the health risks caused by indoor air pollution
can be
reduced, if not avoided or eliminated totally; (4) the need for energy conservation has lead to
reduced
infiltration and ventilation; and (5) synthetic materials with their attendants offgassing have been
used
more and more extensively in homes and offices.
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Guide to Indoor Air Pollutants
3. Definitions
Health: this term is defined by the World Health Organization as "a state of complete physical,
mental,
and social well-being; not merely the absence of disease or infirmity".
Air Quality: the nature of air that affects your health and well-being.
Acceptable Air Quality: air in which there are no known contaminants at harmful concentrations and
with which a substantial majority (usually 80%) of the people exposed do not express
dissatisfaction.
4. Objectives of This Publication
This presentation has two objectives: (1) to educate the public about the nature of the indoor air
pollu-
tion problem and alerting the public to the seriousness and potential danger of the problem; and (2)
to provide information to the public on how to prevent, control and remediate the problem promptly
if
they do arise.
CA
i CA
~
' ~ Cd
~
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Guide to Indoor Air Pollutants
Chapter 11 Indoor Air Pollution in Residential Houses
1. Sources of Indoor Air Pollutants
The gases or particles released by indoor pollution sources into the air are the primary cause of
indoor
air quality problems in homes. The indoor air pollutants can be divided into the following
categories:
a. Oil, gas, kerosene, coal, or wood combustion sources;
b. Building materials and furnishings as diverse as deteriorated asbestos-containing insulation, wet
or
damp carpeting, and cabinet or furniture made of certain pressed wood products;
c. Products for household cleaning and maintenance, personal care, or hobbies;
d. Central heating and cooling systems and humidification devices;
e. Tobacco smoke;
f. Contaminated outdoor air such as pollen, dust, fungal spores, industrial pollutants, general
vehicle
exhaust, odors from dumpsters, re-entrained exhaust from the building itself or from neighboring
build-
ings, unsanitary debris near the outdoor air intake.
g. Soil gas such as radon, leakage from underground fuel tanks, pesticides, previous landfills, etc.
h. Personal activities such as smoking, cooking, body odor and cosmetic odors.
The importance of an individual pollutant source depends on a number of factors such as the amount
of pollutant emission by the source and the level of hazard posed by the pollutant to people. Often,
pollutants released by one single source may not cause a significant risk to the residents, however,
there can be a much more serious health risk to the residents when pollutants are emitted from a
num-
ber of sources and are accumulated in residential houses.
2. Contamination from Outside Sources
Indoor air can also be contaminated from sources outside the house. This occurs primarily when pol-
lutants from automobile exhausts, plumbing vents, and building exhausts enter the building through
improperly located outside intakes, windows, and other openings. In addition, combustion products
such as carbon monoxide and nitrogen dioxide can enter a building from an attached or underground
garage.
3. Ventilation
When the outside air flow through a house is low, the pollutants emitted from various sources in the
homes can accumulate and pose a health problem or discomfort to the residents of homes. There-
fore, exchange of air is very important in reducing indoor air contaminant levels. Some homes are
designed to minimize the amount of air leaking into and going out of them, thus may have a higher
possibility to accumulate indoor air pollutants unless they have a well-designed ventilation system.
However, even homes normally considered "7eaky" can build up the level of pollutants under certain
weather conditions.
1
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Guide to Indoor Air Po11 utants
4. Air Exchanges
Outside air enters a house in three ways: (a) infiltration - air flows through construction joints
and
cracks around windows and doors, in the foundation, or from crawl spaces underneath homes; (b)
natural ventilation - air enters through opened windows and doors; and (c) mechanical ventilation.
When there is little or no air exchange with the outdoors, a building is poorly ventilated, and
indoor air
pollution increases. Therefore, provision of adequate makeup air should be ensured at all times.
5. Assessing Indoor Air Quality in Residential Houses
5.1 Symptoms
If you think that you have symptoms that may be related to the indoor environment in your home, you
should consult your doctor or your local health department whether such symptoms could be caused
by indoor air pollution. You may also want to consult a board-certified allergist or a specialist in
oc-
cupational medicine for answers to your questions. If your symptoms are possibly connected with the
indoor air quality in your home, identify possible sources of contamination.
It is prudent to try to improve the indoor air quality in your home even if symptoms are not
noticeable.
The earliest symptoms of long-term health problems, such as some respiratory illnesses and cancer,
do not appear until years after the initial exposure.
5.2 Identification of Potential Sources
An effective way to judge whether your home has or could develop indoor air problems is to identify
potential sources of indoor air pollution, though the presence of such sources does not necessarily
mean that you have an indoor air quality problem. Being aware of the type and number of potential
sources is an important step toward assessing the air quality in your home.
5.3 Personal Hygiene and Pets
Household pets such as cats and dogs are sources of saliva and animal dander and can cause
serious indoor air quality problems. People and animals are carriers of viruses and bacteria. You
should check your own lifestyle and personal hygiene as they can be significant sources of indoor
air
pollution. -
5.4 Signs of Problem
You should look for signs of indoor air problem including odorous or stuffy air, dirty central
heating
and air cooling equipment, damaged flues and chimneys, moisture condensation on windows or walls,
signs of water leakage, idle water near air intake points outside windows, and areas where books,
shoes, or other items acquire molds. ,
5.5 Measurement of Indoor Air Pollutants
Air testing/measurement is the most effective way to find out the actual level of indoor air
pollutants in
your home, especially when certain health symptoms are noticed and when certain sources of con-
tamination are suspected in your home. Currently, the Federal government recommends that you
measure the level of radon in your home. Though measurement of certain pollutants such as radon
can be performed by yourself with inexpensive devices available on the market, it is recommended
that air testing for your indoor air pollutants should be carried out by an expert in order to
achieve ac-
curate test results and correct interpretations of the results. Such measurements by experts will
also
allow thwm to provide a full range of recommendations to encounter each specific indoor air quality
problem.
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Guide to Indoor Air Pollutants
6. Ways of Improving Your Indoor Air Quality
6.1 Pollutant Source Control
This is the most obvious and effective means of protecting indoor air quality and residents of your
home, especially when specific sources of contamination are identified. With this approach, actions
can be taken to eliminate or reduce the emissions from a pollutant source, and may be used in com-
bination with Increased ventilation to dilute the indoor pollutant level. Specific steps that you
can take
to control individual sources of indoor air pollution in your home are given later in Chapter V,
Com-
mon Indoor Air Pollutants.
6.2 Ventilation Improvement
The level of indoor air pollutants can be reduced by increasing the amount of outside air coming in-
doors by means of natural ventilation and/or mechanical ventilation. When weather permits, natural
ventilation can be increased by opening windows and doors. By turning on a local exhaust fan in the
kitchen or bathroom, you can lower pollution levels by removing contaminants from the room where
the fan is located. Additional ventilation should be provided to dilute or exhaust contaminated air
when you are involved in short-term activities that can generate high levels of pollutants. Another
way
to increase the mechanical ventilation rate is to install heat recovery ventilators in homes. These
devices increase ventilation by drawing outside air into the home and conserve energy by recovering
the heat from air that is exhausted to the outdoors.
6.3 Air Cleaners
They can be used in combination with source control and ventilation. There are many types and sizes
of air cleaners on the market: some of them are highly effective at particle removal, while others,
in-
cluding most tabletop models, are much less efficient. Both the Environmental Protection Agency
(EPA) and Consumer Protection Safety Commission (CPSC) plan to undertake more studies to
evaluate the effectiveness of air cleaners that are on the market today and to identify improvements
in
the way air cleaners can be designed, operated and maintained.
6.4 Education j
This is a very important control method. If home residents fully understand the sources and effects
of
indoor contaminants, they can act together to reduce the indoor pollutant exposures. ;
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Guide to Indoor Air Pollutants
Chapter III Indoor Air Pollution in Office Buildings
1. Background
The air we breathe while at work can affect our job performance, general sense of well being, and
our
health. Twenty-five percent of America's employees work in an office environment with mechanical
heating, ventilation, and air-conditioning (HVAC) systems. An increasing number of these office
employees are experiencing work-related health problems. The problems caused by indoor con-
taminants have become more prevalent within the last 10 years. One primary cause has been the
need to reduce the amount of energy required for heating and cooling office buildings. The method
most often used to reduce this energy consumption has been to "tighten" the building to prevent the
gain or loss of air which requires to be conditioned. Tightly closed buildings prevents the removal
and
dilution by outside air of the pollutants generated by an increasing variety and quantity of
synthetic
materials introduced into the indoor environment. Indoor pollutants, building up faster than they
can
be diluted, result in occupant discomfort and complaints of stuffiness, eye irritation, fatigue,
drowsi-
ness, nausea, and stale air.
The presence of indoor air pollutants has been associated with reports of recent terms such as "sick
building syndrome" and "building-related illnesses". -
1.1 Sick Buildings
A building is characterized as "sick" when its occupants complain of health and comfort problems
that
can be related to working or being in the building.
1.2 Sick Building Syndrome (SBS)
Problems associated with buildings are "sick building syndrome (SBS)". The symptoms of SBS in-
clude:
a. A substantial percentage of building occupants complain of symptoms associated with acute dis-
comfort - headache; eye, nose or throat irritation; dry cough; dry or itchy skin; dizziness and
nausea;
difficulty in concentration; fatigue; and sensitivity to odors.
b. The cause of the symptoms is not known.
c. Most of the complainants report relief upon leaving the building.
1.3 Building Related Illness (BRI)
Problems connected with sick buildings are also called "building related illnesses (BRI)". When oc-
cupant exposure to indoor contaminants results in a clinically defined illness, disease of
infirmity, the
building is said to manifest building-related illnesses. The symptoms of BRI include:
a. Complaints of symptoms such as cough; chest tightness; fever; chills; and muscle aches which can
be associated with illness.
b. The cause or causes of the symptoms are believed to be exposure to indoor pollutants.
c. Complainants may require prolonged recovery times after leaving the building.
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Guide to Indoor Air Pollutants
1.4 Common Air Pollutants and SBS/BRI Symptoms
Common Air Pollutant Symptoms/Effects
Radon Lung Cancer
Volatile Organic Compounds (VC) Irritation; Cancer
Tobacco Smoke
Odors; Bioeffluents
Carbon Monoxide, Carbon
Dioxide, Ozone
Eye, Nose and.Throat Irritation; Lung Cancer
Discomfort
Fatigue, chest pain,
Impaired vision and coordination, nausea,
headache, dizziness, confusion, flu-like
symptoms, weekness, disorientation
Nitrogen Eye, nose and throat irritation, impaired
lung function and increased respiratoryinfection
Microbial Allergens Humidifier Fever; Hypersensitivity Pneumonitis;
Eye, Nose, and' Throat Irritation
Legionella (a bacterium) Legionnaires Disease; Pontiac Fever
Formaldehyde & Other Aldehydes Eye, nose and throat irritation, wheezing
and, coughing,fatigue, skin rash, severe
allegic reactions, may cause cancer
1.5 HVAC System
The HVAC system includes all heating, cooling, and ventilaton equipment serving a building: furnaces
or boilers, chillers, cooling towers, air handling units, exhaust fans, ductwork, filters, steam
piping.
2. Sources of Indoor Air Pollution
Indoor air pollution in offices is caused by an accumulation of contaminants that come primarily
from
inside the building, although some originate outdoors. They may be generated by a specific source
over a wide area, either at certain times or continuously. Contaminants and their sources can
general-
ly be classified into the following categories:
Sources of Pollutants Outside Building
Building Material Sources of Pollution
Building/Office Equipment Sources of Pollution
Maintenance Material Sources of Pollution
Building Inhabitants as Sources of Pollution
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Guide to Indoor Air Pollutants
3. Ventilation Systems
Most mechanical ventilation systems in large office buildings are designed and operated not only to
heat and cool the air, but also to draw in and circulate outdoor air. These units distribute a blend
of
outdoor air and recirculated indoor air. HVAC may also include units that introduce 100% outdoor air
or that simply transfer air within the building. Uncontrolled quantities of outdoor air enter
buildings by
infiltration through windows, doors, and gaps in the exterior construction. Thermal comfort and ven-
tilation needs are met by supplying "conditioned" air (a blend of outdoor and recirculated air that
has
been filtered, heated or cooled, and sometimes humidified or dehumidified).
Properly designed, installed, operated and maintained l-HVAC systems promote indoor air quality.
Poor design, installation, operation or maintenance of such.systems, on the other hand, can create
in-
door air quality problems.
3.1 Inadequate Design or Installation
Indoor air pollution increases when, in an effort to save energy, ventilation systems are not used
to
bring in adequate amounts of outdoor air: (a) Intermittent air flow - designs that operate the HVAC
sys-
tem at reduced or interrupted flow during certain portions of the day in response to thermal
condition-
ing needs, may elevate indoor contaminant levels by reducing air flow and miXing, thus impairing
contaminant removal efficiency; (b) poor air distribution within a room, locating air supply and
return
registers too close to each other can result in poor distribution of fresh dilution air and poor
removal of
indoor air contaminants; (c) poor intake or exhaust location - building exhaust ducts and outside
air in-
takes that are too close to each other can result in re-entry of contaminated exhaust air into the
build-
1ng and a building-up of indoor pollution. Improperly located outside intake air vents can also
bring in
outdoor contaminants and can result in poor intake of outdoor fresh air and recirculation of indoor
air;
and (d) Inadequate space design of modular furniture and walls - overloading limited space without
modifying ventilation system accordingly can lead to poor distribution of air.
3.2 Inadequate Operation
Allowing the system operation to lag behind building occupancy or to be turned down or off before
non-occupancy can increase both building- and occupaht-generated pollutant levels.
3.3 Inadequate Maintenance
If HVAC systems are not properly maintained, their filters can become a source of contamination or
be-
come plugged and reduce air flow. Humidification and dehumidification systems must be kept clean
to prevent the growth of bacteria and fungi. Failure to properly treat cooling tower water to
mitigate
growth of organisms such as legionnella may introduce such biological organisms into HVAC air in-
takes with potentially serious health consequences.
4. Office Equipment As A Source of Indoor Air Pollution
Office Equipment is an important factor affecting indoor air quality. Possible pollutant sources
from of-
fice equipment include (1) emmissions from office equipment (volatile organic compounds,
ozone); (2) supplies (solvents, toners, ammonia); (3) emissions from shops, labs, cleaning
processes;
and (4) elevator motors and other mechanical systems.
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Guide to Indoor Air Pollutants
5. Evaluating Indoor Air Quality in Offices
5.1 Identification of Problems
The investigation starts with written questionnaires and telephone consultations in which building
in-
vestic,iators assess the history of complaints by the building occupants and building operation
proce-
dures. In some cases, personal interviews by the investigator may be needed.
5.2 Symptoms
The effects of IAQ problems are often non-specific symptoms rather than clearly defined illnesses.
These symptoms commonly attributed to IAQ problems include: (1) headache; (2) fatigue; (3) short-
ness of breath; (4) sinus congestion; (5) cough; (6) sneezing; (7) eye, nose, and throat irritation;
(8)
skin irritation; (9) dizziness and (10) nausea. All of these symptoms, however, may also be caused
by
other factors, and are not necessarily due to air quality deficiencies.
lndividuals with these symptoms should be examined by a physician to determine if the symptoms
may be related to the work environment. Consultation with a Board-certified specialist in
occupational
medicine may be advisable.
5.3 Identifying Sources of Pollution
A walk-through should be conducted by the investigator(s) to look for obvious and potential sources
of contamination.
5.4 Qualitative Diagnostics
The investigators characterize the problems and complaints and evaluate the building's environmental
control system design and performance relative to building performance criteria. They may evaluate
the causes of suspected health problems and sample air for suspected pollutants. If discomfort or
SBS is suspected, the investigators may do an engineering analysis of the HVAC system and other
building support systems. If BRI is thought to be the problem, they may recommend immediate medi-
cal assistance along with appropriate biological or chemical sampling.
5.5 Sampling Air for Contaminants and Indicators
Although air sampling might seem to be the logical response to an air quality problem, such an ap-
proach may not be required to solve the problem and can even be misleading. Air sampling should
not be undertaken until some or all of qualitative diagnostic activities mentioned previously have
been
used to collect considerable information. Before beginning to take air samples, investigators should
develop a sampling strategy that is based on a comprehensive understanding of how the buidling
operates, the nature of the complaints, and a plan for interpreting the results.
It may be desirable to take certain routine air quality measurements during an investigation to
obtain a
"snapshot" of current condition. These tests should be limited to those that are indicative of very
com-
mon (AQ concerns such as temperature, relative humidity, air movement, or carbon dioxide (C02).
Unusual readings may or may not indicate a problem, and should always be interpreted in perspec-
tive, based upon site-specific conditions.
5.6 Recommendations
The report of the investigation generally includes a series of recommendations for remedial actions,
maintenance procedures, and building systems operation.
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Guide to Indoor Air Pollutants
6. Resolving Air Quality Problems in Office Buildings
6.1 Pollutant Source Removal, Modification, or Substitution
Resolution of a building which manifests BRI usually requires removal of the pollutant source. This
is
the most effective way to resolve an indoor air quality problem when specific sources causing the
problem can be identified. This approach reduces or eliminates the emission from a pollutant source,
and may be used in combination with increased ventilation to dilute the indoor pollutant level.
6.2 Time of Use Adjustment of a Pollutant Source
When feasible, activities that generates pollutants should be limited to times when the building oc-
cupancy is at minimum, e.g., painting during weekend or non-working hours, and allowing building
materials in new or remodeled areas to off-gas pollutants under high ventilation conditions before
oc-
cupancy.
6.3 Improving Maintenance of Ventilation System
HVAC systems must be properly maintained and operated to avoid accumulation of pollutants and
minimize growth of biological organisms. Inspection of the ventilation system should be conducted
frequently and regularly.
6.4 Increasing Ventilation Rates
In general, Increasing the ventilation rate lessens indoor air quality problems in a poorly
ventilated
building. In buildings with mechanical ventilation systems, outdoor air quantities should be
provided
at rates at least as high as those specified in appropriate standards or codes. The American Society
of Heating, Refrigerating and Air Conditioning Engineers (ASHRAE) proposed ventilation standard 62-
1989 specifies a minimum of 20 cfm per person for offices. Optimally, local exhaust should be
employed to remove indoor pollution near such sources as restrooms, copying rooms, and printing
facilities.
6.5 Air Filtration and Purification
These processes can be used in combination with source control and ventilation where specific
problems are identified and practical air cleaning options exist. There is a wide range of such
devices
available on the market, but increased performance can involve significantly higher costs.
6.6 Communication
Effective communication can encourage building occupants to improve their work environment
through positive contributions. The following objectives should be kept in mind while reviewing and
revising your current approach to communicating with occupants: (1) provide accurate information
about factors that affect indoor air quality; (2) clarify the responsibilities of each party
including build-
ing management, staff, tenants, contractors, etc.
7. Control Process of Indoor Air Pollution in Buildings
The process of controlling indoor air pollution in buildings is divided into a number of specific
steps. A
model process of this process is illustrated in Figure 1.
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Guide to Indoor Air Pollutants
8. Professional Help
Frequently indoor air quality problems in large commercial buildings cannot be effectively
identified or
remedied without a comprehensive building investigation. The process of solving indoor air quality
problems that result in health and comfort complaints can be a slow one, sometimes involving several
trial solutions before successful remedial actions are identified. To successfully resolve indoor
air pol-
iution problems in office buildings therefore often requires the expertise of an indoor air quaiity,
specialist and a number of specialists. Whether or not an external specialist is needed to solve an
in-
door air quality problem depends on the expertise of the facilities engineering and environmental
health staff. A considerable amount of literature is available for the guidance of in-house
activities.
However, when such in-house expertise is not available and not sufficient to cope with the existing
scale of the problem, it is strongly recommended that external professional help be used.
Firms and individuals working in IAQ may come from a variety of disciplines. Typically, the skills
of
HVAC engineers and industrial hygienists are useful for this type of investigation, although input
from
other disciplines such as chemistry, chemical engineering, architectiure, microbiology, or medicine
may also be important.
If problems other than indoor air quality are involved, experts in lighting, acoustic design,
interior
design, psychology, or other fields may be helpful in resolving occupant complaints about the indoor
environment.
As you prepare to hire professional services in the area of indoor air quality, be aware it is a
develop-
ing area of knowledge. Most consultants working in the field received their primary training in
other
areas. A variety of investigative methods may be employed, many of which are ineffective for resolv-
ing any but the most obvious situations. Inappropriately designed studies may lead to conclusions
that are either false negative or false positive.
A qualified IAQ investigator should have apprpriate experience, demonstrate a broad understanding of
indoor air quality problems and the conditions which can lead to them, and use a phased diagnostic
approach.
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Guide to Indoor Air Pollutants
Figure 1: Process for Control of Indoor Air Pollution in Buildings
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Guide to Indoor Air Pollutants
Chapter IV Evaluation Criteria for Indoor Air Quality
1. Public Health Standards
Public health standards are more frequently used to address indoor air quality problems. Some of
them are as follows:
1.1 National Ambient Air Quality Standards Established by the US Environmental Protection Agency
Enforcement is limited to outdoor ambient levels. The standards specify concentrations of pollutants
in ambient air that should not be exceeded. However, these standards may not have relevance to an
indoor office environment, especially from the perspective of problem-solving.
1.2 WHO Air Quality Guidelines for Europe
The Regional Office for Europe of the World Health Organization (WHO), an agency of the United Na-
tions, recently published air quality guidelines for 28 organic and inorganic substances. The
guidelines were created to help governments make risk management decisions controlling exposure
to indoor and outdoor air pollutants. Health effects were the major consideration in establishing
the
guidelines. Guidelines are set to protect all people In the European region, including sensitive
popula-
tion subgroups such as asthmatics. Both short- and long-term exposures are addressed (WHO,
198i'). '
1.3 ASHRAE Standard 62-1989: Ventilation for Acceptable Indoor Air Quality
American Society of Heating, Refrigerating and Air-Conditioning Engineers (ASHRAE) Standard 62-
1989 defines acceptable indoor air quality as "air in which there are no known contaminants at
harmful
concentrations as determined by cognizant authorities and with which a substantial majority (80% or
more) of the people exposed do not express dissatisfaction. The objective of the standard is to
estab-
lish minimum ventilation rates and indoor air quality that will be acceptable to human occupants and
are intended to avoid adverse health effects. The ASHRAE standards cover 35 substances. For con-
taminants not contained in the standard, ASHRAE recommends that levels should not exceed 1/10 the
occupational standard used in the industry. These standards are frequently used by IAQ specialists
in
office building evaluations, especially for assessing the performance of a ventilation system.
ASHRAE
standards are also commonly used as criteria for assessing the thermal performance of occupied
space.
1.4 Canadian Exposure Guidelines for Residential Indoor Air Quality (Excluding Radon)
The guidelines were published in 1987. The guidelines contain specific quantitative limits for nine
pof-
lutants or pollutant categories, plus recommendations to eliminate or control exposure for other
pol-
lutants for which specification of exposure limits was not practical. Their application is designed
for
residential environments, and is based on assumptions of 24-hour exposure. The guidelines may not
provide complete protection to the hypersensitive portion of the population. Effects from both
short-
term and long-term exposures are covered.
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Guide to Indoor Air PoEfutants
2. Occupational Health Standards
in the classic industrial hygiene sense, the Occupational Safety and Health Administration's (OSHA)
permissible exposure limits (PEL), the American Conference of Governmental Industrial Hygienists'
(ACGIH) Threshold Limit Values (TLV), and National Institute of Occupational Safety and Health's
(NIOSH) recommended exposure limits (REL) are most commonly used in occupational exposure as-
sessments. Because these criteria are based on health effects as they pertain to the manufacturing
en-
vironment, they may not have the same relevance for workers in an office setting, whose primary
concern may be for comfort or simply an absence of unusual sensory stimuli over their working
period. Although these standards may not be directly relevant to the indoor office environment, they
may be used as a starting point and a guideline in the evaluation of indoor air quality of offices.
3. Evaluation of Existing Standards and Guidelines
Several points emerge from the evaluation of existing standards and guidelines. These include (1)
the
difference between public health and occupational standards; and (2) major omissions among existing
standards with regard to indoor air quality problems.
3.1 Public Health Standards vs. Occupational Health Standards
The most significant differences between various standards and guidelines are related to the
differen-
ces between standards set to protect the general public versus those set to protect workers in an
oc-
cupationall setting. Public health standards are generally one to two orders of magnitude lower than
occupational standards. These differences occur for both short- and long-term exposure limits. Some
of the reasons for these differences are (1) public health standards include protection for the
sensitive
population subgroups, while occupational standards typically presume a healthy adult workforce; (2)
public health standards generally assume continuous exposures while occupational standards are
based on 8 hours exposure period per day for no more than 40 hours per week; (3) public health
standards are usually established with adverse health concerns as the sole criteria.
3.2 Regulatory Gap
Two areas of particular concern in indoor air quality have yet to be adequately addressed by
existing
standards and guidelines. These include exposure to pollutant mixtures and to biological con-
taminants (e.g., molds, fungi, mites, bacteria, and viruses).
The effects of exposure to more than one contaminant in indoor air is an important issue since the
typi-
cal indoor environment contains multiple contaminants. Effects from mixtures may be synergistic, an-
tagonistic, or additive.
Existing standards and guidelines do not address biological contaminants, yet biological con-
taminants pose potentially significant problems for indoor air quality.
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Guide to Indoor Air Pollutants
Chapter V Common indoor Air Quality, Measurements
1. Common Sampling Devices
1.1 Vacuum Pump
A vacuum pump with a known airflow rate draws air through collection devices, such as a filter, a
sor-
bent tube, or an impinger. Tests originated for industrial environments typically need to be
adjusted to
a lower detection limit for IAQ work. Labs can be asked to report when trace levels of an
identifiable
contaminant are present below the limit of quantification and detection.
1.2 Direct-reading Meter
Direct-reading meters estimate air concentrations through one of several detection principles. These
may report specific chemicals, chemical groups, or broad pollutant categories. 'Detection limits and
averaging time developed for industrial use may or may not be appropriate for IAQ.
1.3 Detector Tube Kit
Detector tube kits generally include a hand pump that draws a known volume of air through a chemi-
cally treated tube intended to react with certain contaminants. The length of color stain resulting
in the
tube correlates to chemical concentration.
1.4 Personal monitoring devices
Personal monitoring devices area carried or worn by individuals and are used to measure that
individual's exposure to particular chemical(s). Devices that include a pump are called "active"
monitors; devices that do not include a pump are called "passive" monitors. Such devices are
current-
ly used for research purposes. It is possible that sometime in the future they may also be helpful
in
IAQ investigations in public and commercial buildings.
1.5 Thermometer and Sling Psychromter
These simple devices can be used to measure indicators of thermal comfort including temperature
and relative humidity.
1.6 Chemical Smoke
Chemical smoke can be helpful in evaluating HVAC systems, tracking potential contaminant move-
ment, and identifying pressure differentials. Chemical smoke moves from areas of higher pressure to
areas of lower pressure if there is an opening between them. Because it is heatless, chemical smoke
is extremely sensitive to air currents. Chemical smoke is available with various dispensing
mechanisms, including smoke "bottles," "guns," "pencils," or "tubes:'
2. Measurement of Air Flow and Outdoor Air Quantities
2.1 Airflow
Measurement of airflow allow investigators to estimate the amount of outdoor air that is entering
the
building and to evaluate HVAC system operation. Airflow quantities can be calculated by measuring
the velocity and cross-sectional area of the airstream. For expample, if air is moving at 100 feet
per
minute in a 24" x 12" duct, the airflow is:
100 feet/minute x 2 square feet duct area = 200 cubic feet/minute.
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Guide to Indoor Air Pollutants
Air velocity can be measured with a pitot tube or anemometer. Air velocity within an airstream is
likely
to vary considerably. The best estimates of air velocity can be achieved by averaging the results of
a
number of measurements. ASTM Standard Practice D3154 provides guidance on making such meas-
urements.
2.2 Outdoor Air Quantities
Outdoor air quantities can be evaluated by measuring airflow directly. Two frequently used
techniques
are thermal mass balance (temperature) and Carbon Dioxide Measurements. Outdoor air quantities is
calculated as follows:
Using Thermal Mass Balance
Treturn air - Tmixed air
Outdoor air (percent) = -~~ - ______ x 10b
return air - outdoor air
Where: T = temperature (degrees Farenheit)
Using Carbon Dioxide Measurements
CS-CR
Outdoor air (percent) = x 100
Co - CR
Where: Cs = ppm C02 in the supply air (if measure in a room), or
Cs = ppm of C02 in the mixed air (if measured at an air handler)
CR = ppm of C02 in the return air
Co = ppm of C02 in the outdoor Air
Converting Percent to CFM
Outdoor air (percent)
Outdoor air (cfm) =x total airflow (cfm)
100
Where: cfm = cubic feet per minute
The number used for total airflow may be the air quantity supplied to a room or zone, the capacity
of
an air handler, or the total airflow of the HVAC system.
3. Air Contaminant Concentrations
3.1 Total Volatile Organic Compounds (TVOCs)
N
Several direct-reading instruments are available that provide a low sensitivity "total" reading for
dif- ~
ferent types of organics. Such estimates are usually presented in parts per million and are
calculated ~
with the assumption that all chemicals detected are the same as the one used to calibrate the
instru- ~
ment. A laboratory analysis of a sorbent tube can provide an estimate of total solvents in the air.
4
~
~
~
00
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Guide to Indoor Air Pollutants
3.2 Individual Volatile Organic Compounds (VOCs)
Individual VOCs can be measured in indoor air with a moderate degree of sensitivity through adapta-
tions of existing industrial air monitoring technology. Examples of medium sensitivity testing
devices
include XAD-4 sorbent tubes, charcoal tubes, and chromosorb tubes. AFter a sufficient volume of air
is pumped through these tubes, they are sent to a lab for extraction and analysis by gas chromatog-
raphy. Variations use a passive dosimeter to collect the sample or a portable gas chromatograph on-
site for direct injection of building air. These methods may not be sensitive enough to detect many
trace level organics present in building air.
High sensitivity techniques have recently become available to measure "trace organics" - VOCs in the
air. Sampling may involve Tenax and multiple sorbent tubes, charcoal tubes, evacuated canisters, and
other technology. Analysis involves gas chromatography followed by mass spectroscopy.
3.3 Formaldehyde
Formaldehyde is a VOC that has been studied extensively. Two commonly used methods that are
generally acceptable for IAQ screening involve impingers and sorbent tubes.
3.4 Biological Contaminants
No single technique is effective for sampling the many biological contaminants found in indoor
environ-
ments. A variety of specific approaches are used to retrieve, enumberate, and identify each kind of
microorganism from water, surfaces, and air. Other specific methods are used for materials such as
feces or insect parts. Where air sampling is desired, several approaches are available. The most
com-
mon type of air sampler uses a pump to pull air across a nutrient agar, which is then incubated. Any
bacterial or fungal colonies that subsequently grow can be counted and identified by a qualified
microbiologist. Different types of agar and incubation temperatures are used to culture different
types
of organisms. Only living organisms or spores in the air are counted by this method.
3.5 Airborne Dust
Dust can be collected by using a pump to draw air through a filter. The filter can then be weighed
or
examined under a microscope.
3.6 Combustion Products
Direct-reading meters, detector tubes, and passive dosimeters are among the techniques most com-
monly used to measure carbon monoxide and nitrogen oxides.
3.7 Other Inorganic Gases
Although they are not routinely sampled in most lAQ studies, a variety of other gases may be
evaluated where conditions warrant Examples might include ammonia, ozone, and mercury.
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Guide to Indoor Air Pollutants
Chapter VI Common Indoor Air. Pollutants
This chapter provides specific information on each common indoor air pollutant listed below. The
informa-
tion provided is meant to be used as a guideline when dealing with these pollutants.
1. List of Common Indoor Air Pollutants
Contaminant Sources
Acetic acid
Acetone
Acrolein
Aldehydes
Alkyl benzene sulfonate
Alkyl aryl sodium sulfonate
Ammonia
Amines
Ammonium Compounds
Asbestos
Asbestos Fibers
Anthophylite
Chrysotile
Crocidolite
Tremolite
Bioaerosols
Algae
Arthropods
Bacteria
Fungi
Greenplants
Mammals
Protozoa
Borax
Butyric acid Engineering drawing/copying machine
Bioeffluents
Smoking
Exhaust of gasoline and diesel engines outdoors,
tobacco smoke
Commercial cleaning products
Commercial cleaning products
Microfilm machines Engineering drawing
reproduction machines ,
Humidification equipment
Commercial cleaning products
Draperies, filters, stove mats, Actinolite floor tile,
spackling compound, Amosite furnaces (older), roofing,
gaskets, insulation, acoustical materials, talcum powder,
ironing board cover, hot mittens, hair dryers (old)
utdoor air -
House dust
Cooling towers, hot water sources, hot damp surfaces,
stagnant water reservoirs, industrial processes
Damp environmental surfaces, outdoor air, damp surfaces,
bird droppings
Outdoor air
Horses, cats
Contaminated water reservoirs
Commercial cleaning products
Bioeffluents
Carbon Photocopying machines
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Guide to Indoor Air Pollutants
Combustion Products
Carbon Monoxide
Carbon Dioxide
Sulfur Dioxide
Nitrogen dioxide
Respirable particles
Benzo(a)pyrene
Hydrogen Cyanide
Diethyl ethanolamine
Ethyl alcohol
Formaldehyde
Kerosene
Lead
Man-made mineral fibers
Methyl alcohol
Methylacrylates
Naphtha
Nicotine
Organics
Benzaldehyde
Benzene
n-Butylacetate
Cumene
Cyclohexane
Cyclohexanol
n-Decane
Diethyl phthalate
Dodecane
Ethylbenzene
1 -Ethyl-2-methylbenzene
1 -Ethyl-4-methylbenzene
n-Heptane
Limonene
Menthone
Mesitylene
Methylene chloride
1-Methyinaphthalene
2-Methyi-naphthalene
Naphthalene
Organics Cont.
Combustion sources including: gas ranges, dryers,
water heaters, kerosene heaters, fireplaces and
woof stoves, gas stoves, garages, outdoor sources,
chimneys, furnaces
Boiler additive
Bioeffluent
Particle board, urea-formaldehyde insulation,
pressed wood, plywood resins, hardwood paneling,
carpeting, upholstery, paper towels, disinfectants, carpet
shampoos, toothpaste, smoking, grocery bags, waxed
paper, facial towels, shampoo, cosmetics, medicines
Commercial cleaning products
Automobile exhaust, sanding or open-flame burning
of lead-based paint, activities involving lead
solder, outdoor sources
Fiberglass insulation, mineral wool insulation
Spirit duplication machine, bioeffluent
Signature machine
Commercial cleaning products
Tobacco smoke
Varnishes, paints, polishes, cleaners, etc.
22 Detail Associates, Inc.

Nonane
n-Octane
n-Pentadecane
Propylbenzene
Tetradecane
1,1,1 -Trichloroethane
Toluene
n Tridecane
o,m,p-Xylene
Organic vapors
Ozone
Pine oil
Pesticides
Aldrin
Chlordane
Dieldrin
Heptachlor
Petroleum solvents
Polychlorinated biphenyls (PCBs)
Radon decay products
Sodium carbonate
Sodium perborate
Sodium phosphates
Sodium dodecyl sulfate
Trinitrofluorene
Trinitrofluorenone
Vinyl chloride
Guide to Indoor Air Pollutants
Carpet adhesives, wool finishes
Electrical equipment, electrical air cleaners, outdoor sources
Commercial cleaning products
Products used to kill household pests, and products
used on lawns and gardens that drift or are tracked
inside the house
Commercial cleaning products
Carbonless carbon paper
Concrete, brick, stone, soil, ground water, shower/hot
wash water
Commercial cleaning products
Commercial cleaning products
Commercial cleaning products
Carpet shampoo
Photocopying machines
Photocopying machines
Aerosol spray, propellants, and solvents
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Guide to Indoor Air PoIIutants
2. Biological Contaminants
2.1 Biohazard:
Biohazard is a combination of the words biological hazard and refers to plants, animals of their
products that may present a potential risk to the health and well-being of humans or animals.
Biohazard can affect humans either directly through illness or indirectly through disruption of the
en-
vironment. Biohazard can be transmitted to a person through inhalation, injection, ingestion, or
con-
tact with the skin.
2.2 Bioaerosols:
Bioaerosois are airborne particles, large molecules, or volatile compounds that are living or were
released from a living organism. Figure 2 gives examples of common bio-aerosol sources and their
nature of pollution.
2.3 Some Factors Affecting indoor Microbial Levels
(1) Humidity: levels between 25% - 70% can allow fungal growth; less than 70% optional to support
fungal growth
(2) Water: ponds, humidifiers, HVAC, building leaks
(3) Carbon Sources: decaying plants, soil, cellulose and plant lignins, fabrics, leather; wood and
skin
scales
2.4 Possible Means of Reducing Exposure
(1) Remove stagnant water and slimes from mechanical systems;
(2) Apply chlorine solution when mechanical system is off;
(3) Eliminate water sprays;
(4) Substitute steam for cold water humidifiers;
(5) Eliminate mist vaporizers;
(6) Repair water leaks;
(7) Keep indoor relative humidity below 70%;
(8) Discard porous building materials and any furnishings contaminated with fungi;
(9) Upgrade collection efficiency of air handling filters;
(10) Provide suitable amount of outdoor air.
2.5 Common Air Samplers Used for Indoor Bio-aerosoi Collection
Please see Figure 3 for air samplers commonly used for'collection of indoor bio-aerosols.
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Guide to Indoor Air Pollutants
Sources of Pollution
Air Handling Unit (cooling coil)
Air handling and fan coil units (filters)
Air handling unit (Air washer and water spray
system section)
Fan coil units; induction units
Humidifiers containing reservoirs of stagnant water
Steam humidifier
Porous man-made insulation in ventilation system
Outdoor air intake of ventilation system
Outdoor air
Nature of Pollution
Amplification of microorganisms may occur on
wetted surfaces of cooling coils and in drain pans
Filters may act as reservoirs for microbial
pollutants; amplification can occur if humidity is
excessive or if filter is wetted
Microorganisms grow on wetted mechanical
surfaces, in water reservoirs, and on porous
substrates associated with these devices
These devices may serve as reservoirs for
microbial contaminants; check for accumulated
dust and debris
Organic dusts and, debris are scrubbed from the
air stream; microorganisms may amplify in water
reservoir and on wetted surfaces of device
Condensed water from improperly trapped
devices may serve as a niche for amplification of
microorganisms
Dirt and debris are.trapped in porous areas; can
become microbial reservoir; if insulation is
wet, microbial amplification can occur.
Bioaerosols from nearby cooling tower, evaporative
condensers, and sanitary stacks mayenter out-
door air intake; outdoor air intakes located at
ground level are prone to microbial contamination
from soil and vegetable debris
Outdoor bioaerosols are the ultimate source of
most indoor contaminants.
Figure 2 Sources of Indoor Bio-aerosols and Contamination
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Guide to IndoorAir Pollutants
Sampler Type Principles of Operation Sampling Rate (!pm*) Recommended Sampling Time
1. Slit impactor
2. Sleve Impactor Impaction on rotating or
stationary plate 30-700
continuous 1-60 min or 7 day
a. single-stage
portable Impaction on agar
"rodac" plate 90 or 185 0.5 or 0.3 min
b. single-stage
impactor Impaction on agar;
100 mm plates 28 1 min
c. two-stage
impactor Impaction on agar;
2-100 mm plates 28 1-5 min
3. Filter cassettes Filtration 1-2 15-60 min or 8 hr
4. High-volume
filtration Filtration 140-1400 5 min-24 hr
5. High-volume
electrostatic Electrostatic
collection into liquid up to 1000 variable
6. All-glass
Impingers Impingement into
liquid 12.5 30 min
7. Centrifugal
lmpactor Impaction on agar
plastic strips 40?? 0.5 min
* !pm = liters per minute
Figure 3 Samplers Commonly Used for Collection of Indoor Bioaerosols
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Guide to Indoor Air Pollutants
BACTERIA
GENERAL CHARACTERISTICS
Bacteria are simple, one-celled organisms that are visible only under the microscope and multiply by
simple division or fission into two parts. Bacteria can take the form of very small spheres (cocci),
straight rods (bacilli), spiral rods (spirilli), or long branched filaments (actinomycetes). Most
are in the
size range of 1-5 um, though few are smaller or larger. Some bacteria form long, permanent, branch-
ing chains of cells, mimicking the fungi.
Bacteria of importance in indoor air quality are classified by Gram stain reaction, shape, oxygen
re-
quirements, ability to produce spores, ability to utilize specific substrates, production of
specific meta-
bolites, and ability to cause specific diseases. Please see Figure 4.'
Bacteria metabolize carbon compounds either in the presence of oxygen (aerobically) or in the ab-
sence of oxygen (anaerobically), or both. They excrete complex biochemical products that are in-
strumental in the decay of nonliving organic material. A few bacteria are obligate pathogens and
require a living host. Many are facultative pathogens, able to live either in a living host or on
nonliving
organic material. Many bacteria can be killed by antibiotics which selectively kill prokaryotic
cells. Be-
cause they are saprophytic, most bacteria can be grown in culture and, providing nutritional
require-
ments are met, can be collected from air, cultured, counted, and identified.
Most environments contain a wide variety of bacteria. The types and concentrations are influenced by
prevailing conditions. In general, the human-source bacteria are dominant indoors while the gram-
negative leaf surface organisms are most abundant outdoors. Risk of illness increases only when bac-
teria that can produce disease are selectively amplified in an environmental reservoir and these
organisms or their products become airborne and successfully reach the breathing zone of suscep-
tible humans.
HEALTH EFFECTS
Airborne bacterial cells cause infectious disease by entering the respiratory system of the host.
Legionnaires' disease, other pneumonia, and tuberculosis are common airborne infectious diseases
caused by bacteria. Bacterial cells and their products can also cause humidifier fever and hypersen-
sitivity pneumonitis. Recently, anecdotal evidence has begun to accumulate that bacteria (and fungi)
release organic volatiles that may induce the nonspecific symptoms commonly associated with sick
building syndrome.
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Guide to Indoor Air PolIutants
Page 2
MEANS OF REDUCING EXPOSURE
1.If human-source, nonpathogenic bacteria are abundant, it may be appropriate to increase outside
air
ventilation rates;
2.if indoor air is improperly distributed, ventilation patterns can be altered;
3.Cooling-coil drip pans should be cleaned with oxidants, drains should be cleared, and pans should
be slanted toward drains;
4.Cooling towers should be maintained free of bacteria slimes and their effluent should not enter
breathing air;
5.Humidifiers should be maintained free of scale and slime at all times;
6.Home devices, especially those releasing a droplet spray, should be emptied and dried daily and
cleaned with bleach (5%) or 3% hydrogen peroxide every third day.
MONITORING AND MEASUREMENT METHODS
All of the samplers listed in Figure 3 could theoretically be used to sample for bacteria. For
detailed in-
formation, consult "Guidelines For the Assessment of Bioaerosols in the Indoor Environment", ACGIH,
1989.
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Guide to Indoor Air Pollutants
Organism Gram Shape Oxygen Spore Disease Occurrence in Air
Outside Inside
Legionel9a
pneumonophila
Pseudomonas
- Rods
Rods Oxidative No
Oxidative No Legionellosis
Pneumonia Rare Rare
Occasional Rare
Enterics - Rods Fermentative No Various Rare Rare
Bacillus + Rods Oxidative/ Yes
Fermentative Hypersensitivity Common Common
pneumonitis
Micrococcus + Cocci Oxidative No Usually none Common Common
Mycobacterium {+) Irregular rods Oxidative No Tuberculosis Common Common
Thermoactino-
myces + Branchin Oxidative Yes Hypersensitivity Rare Rare
Corynebacterium (+) Rods Oxidative/ No Usually none Rare Occasional
Fermentative
Figure 4 Classification of Some bacterial Common in Indoor Air or Causing Airborne Disease
I
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Guide to Indoor Air Pollutants
FUNGI
GENERAL CHARACTERISTICS
Fungi are eukaryotic organisms. Fungus cells are bound by rigid walls that, unlike those of plants,
are
formed of acetylglucosamine polymers. Fungi also lack chlorophyll. Fungi can be either unicellular
or
multicellular. The yeasts are unicellular fungi that reproduce primarily by budding. Most fungi,
how-
ever, are formed of long chains of cells called hyphae; a mass of hyphae is called a mycelium.
Mycelial fungi include all the "molds" as well as mushroom, puffballs, shelf fungi, morels, etc.
Most
fungi produce spores designed to be transported through the air.
All fungi are heterotrophic, which means they cannot make their own carbohydrates from water and
carbon dioxide as can the plants, and they must have external food sources. In addition, fungi need
a
sources of nitrogen and many have specific mineral requirements. Fungi are either saprophytic,
parasitic, or both. Saprophytic organisms utilize dead organic material for food. Almost all fungi
can
grow saprophytically. Organisms that live on other living organisms are called parasites.
In the process of degrading substrates, fungi produce many metabolic products, some of which may
affect indoor air quality and certainly have had an impact on humanity.
Environmental factors that influence the distribution of fungi include water, nutrients,
temperature, and
light. Almost any carbon-containing material can provide nutrients to the saprophytic fungi. Water,
on
the other hand, is not always readily available. The intrusion of water into the indoor environment
is
the single most important cause of fungal contamination. If the indoors can be kept dry, fungal
growth
can be essentially prevented. Since fungi are disseminated primarily through the air, and often over
long distances, fungi can be formed throughout the world. They are truely ubiquitous.
HEALTH EFFECTS
Only a few fungi can invade living cells and cause infectious disease. Such infections usually occur
only in people with some immune system dysfunction. Most fungi produce proteins that are highly an-
tigenic and can cause hypersensitivity diseases in susceptible hosts. Figure 5 summarizes informa-
tion on the health effects and environmental sources of various fungi.
MONITORING AND MEASUREMENT METHODS
Air sampling for fungi is often difficult and expensive, and a single sampling modality Is rarely
suffi-
cient. Air sampling is generally useful only to demonstrate that a presumed source is contributing
to
the bioaerosol. Refer to "Guidelines For the Assessment of Bioaerosois in the Indoor Environment",
ACGIH, 1989 for further information.
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Organism Causal Part Disease
Histoplasma Spores
Cryptococcus Spores
Aspergillus Spores
Aspergillus Spores
Penicillium
Sporobolomyces
All airborne fungus Spores
spores
Aspergillus flavus Toxin
Stachybotrys atra Toxin
Ulocladium VOC*
Penicillium species VOC*
`VOC = volatile organic compounds
Histoplasmosis
Cryptococcosis
Invasive aspergillosis;
aspergilloma; allergic
brochopulmonary
aspergillosis (ABPA)
Hypersentivity pneumonitis (HP)
Allergic asthma; Rhinitis
Cancer
Acute Toxicosis
Headache
Irritants
Guide to Indoor Air Pollutants
Usual Source
Bird droppings
Bird droppings
Self-heated compost;
damp organic material
Damp organic material;
outdoor air
Damp organic material;
outdoor air
Agricultural products
Damp cellulosic material
Damp organic material
Damp organic material
Figure 5 Health Effects and Sources of a Few Fungi
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Guide to Indoor Air Pollutants
BIOCIDES
GENERAL CHARACTERISTICS
A biocide is a substance that kills living cells. Biocides are used to disinfect (kill pathogenic
agents by
direct chemical or physical means) and to sanitize (reduce the microbial burden of objects to a
level
prescribed by public health regulations or hygienic considerations).. Biocides that are integrally
at-
tached to materials acting as permanent sanitizers. -
Factors affecting the capacity of a biocide to perform efficiently include concentration of the
biocide,
temperature and pH (hydrogen ion concentration) at which it is used, and ability to combine with or-
ganic material.
H EALTH EFFECTS
Biocides, by definition, kill living cells. They are considered poisons by the EPA. Biocides should
be
used with extreme caution and only when other measures are not sufficient to eliminate or control
the
identified problem. Figure 6 illustrates the major categories of some commonly used biocides and the
principal human health effects of each.
MEAN z OF REDUCING EXPOSURE
Three government agencies regulate biocides in the United States. They include the Environmental
Protection Agency (EPA) which regulates biocides used on inanimate surfaces and registers them as
pesticides; the Food and Drug Administration (FDA) which regulates biocides used on the skin or
mucous membranes; and the Consumer Products Safety Committee (CPSC) which regulates biocides
used on sleepwear, carpeting, etc..
Biocides should not be used unless other measures fail to eliminate or control the problem.
It is important to verify the product registration with the applicable above mentioned agencies
before
using a commercial biocide.
Label instructions on the commercial biocide products should be read carefully and understood clear-
ly before use. These instructions of use should be followed at all times.
MONITORING AND MEASUREMENT METHODS
For detailed information, consult "Guidelines For the Assessment of Bioaerosols in the Indoor
Environ-
ment", ACGIH, 1989.
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Guide to Indoor Air PolIutants
I
Biocides Sporicidal
Activity Mechanism Human Health Effects
(inhalation/Contact)
Hypochlorites Yes Enzyme inactivation irritant, corrosive
Hydrogen peroxide ? Hydroxyl-free radicals None for 3 percent
solution
Quaternary ? Increase cell Toxic irritants
ammonium membrane
compounds permeability
Alcohols No Denatures proteins None reported
(ethanol)
(propanol)
(isopropanol)
Phenolics No Denatures proteins Odor, toxic, irritant, corrosive
Glutaraldehyde Yes Protein cross linking Toxic irritant
Iodine, Yes lodination and oxidation Skin, mucous membrane irritant
lodophors of proteins
Formaldehyde ? Binds DNA, cell proteins Odor, toxic irritants,
may be carcinogeni
Figure 6 Characteristics of Some Common Biocides
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Guide to Indoor Air Pollutants
VIRUS
GENERAL CHARACTERISTICS
Viruses are replicating microorganisms that are the smallest of all life forms. Viruses are a
heterogenous class of microbial agents. They vary in size and morphology, chemical composition,
host range, and in the effect they have on their hosts. Viruses are obligate parasites in that they
must
be associated with a cell to function, which means they are incapable of growth or reproduction
without living cells. Viruses are subdivided into three main classes: animal viruses, plant viruses,
and
bacterial viruses (bacteria-phage). Within each class, a particular virus is normally able to infect
only a
certain species of cells. Viruses have the ability to change and adapt to changes in the
environment.
Viruses occur in many shapes and sizes, but all viruses are constructed according to certain
principles.
HEALTH EFFECTS
The virus particle itself is the inert form of the virus. When a virus particle and a suitable host
cell inter-
act, a virus - cell complex is formed and the fate of that interaction varies widely. Most viruses
enter
the host through following portals of entry: 1) skin; 2) respiratory tract; 3) alimentary tract; 4)
urogeni-
tal tract; and 5) conjunctiva. Successful infection results in damage to the host that can be un-
detected, mild, severe, fatal, teratogenic, behavioral, or result in tumor formation.
MONITORING AND MEASUREMENT METHODS
Instrumentation used to collect bacteria, pollen, and fungal spores can also be used with minor
modifications to collect virus aerosols. Techniques generally used involve sedimentation,
filtration, im-
pingement, impaction, electrostatic precipitation, and scrubbing. For detailed information, consult
"Guidelines For the Assessment of Bioaerosols in the Indoor Environment", ACGIH, 1989.
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Guide to Indoor Air Pollutants
3. Other Common Indoor Air Pollutants
This Section includes specific information on each pollutant listed in the section 1 except
biologicals.
Biological contaminants are discussed in Section 2.
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Guide to Indoor Air Pollutants
ACETIC ACID
MF: C2H402 MW: 60.06
1 DENTf FICATION
Cas #: 64-19-7 NIOSH: AF1225000
SYNONYMS
Acetic acid (aqueous solution) (DOT), acetic acid, glacial (DOT), ethanoic acid, ethylic acid,
glacial
acetic acid, methanecarboxylic acid, octowy kwas (polish), vinegar acid
APPEARANCE OI DOR
Clear, colorless liquid; pungent odor
CHEMICAL/PHYSICAL PROPERTIES
Boiling Point: 118.1 C
Melting Point:.16.7 C
Vapor Pressure: 11.4 mm Hg @ 20 C
Specific Gravity: 1.049 @ 20 C/4 C
Odor threshold: 0.074 ppm - detection threshold
SOURCES OF CONTAMINATION
Engineering drawing copying machines.
EXPOSURE LIMITS
OSHA PEL: TWA: 10 ppm (25 mg/cu m)
NIOSH REL: TWA: 10 ppm (25 mg/cu m) STEL: 15 ppm (37 mg/cu m)
ACGIH TLV: TWA: 10 ppm (25 mg/cu m) STEL: 15 ppm (37 mg/cu m)
EPA Ambient Air Standard: none established
TOXICITY
Inhalation-human TCLo: 816 ppm/3 min
Inhalation-rat LCLo: 16000 ppm/4 hrs
Inhalation-rat LC50: 5620 ppm/1 hr
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I
Page 2
HEALTH HAZARDS
A human poison by an unspecified route. Moderately toxic by various routes. A severe eye and skin
ir-
ritant. Human systemic effects by ingestion: changes in the esphagus, ulceration or bleeding from
the
small and large intestines. Human systemic irritant effects and mucous membrane irritant. Experimen-
tal reproductive effects. Mutagenic data. A common air contaminant.
POSSIBLE MEANS OF REDUCING EXPOSURE
1. To investigate general ventilation rates;
2. To investigate the possibility of local ventilation above the machine.
3. To locate the machine at a location where the pollution and exposure can be minimized; or
possibly
to confine the machine to specially partitioned rooms or compartments to prevent it from polluting
the
larger, general-use habitable space;
4. To find out if the manufacturer has introduced any modifications for reducing pollutant emission
of
the product; if no, search for a manufacturer that does
5. Proper operation and maintenance of the machine.
MONITORING AND MEASUREMENT METHODS
NIOSH Method 1603, third edition
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Guide to Indoor Air Pollutants
ACETONE
MF: C3H60 MW: 58.09
IDENTlFICATION
Cas #: 67-64-1 NIOSH: AL3150000
YN NYMS
Dimethylketal, dimethylformaidehyde, dimethyl ketone, ketone propane, beta-ketopropane, methyl
ketone, propanone, 2-propanone, pyroacetic acid, pyroacetic ether.
APPEARANCE/ODOR
Colorless liquid, fragrant mint-like odor
CHEMICAUPHYSICAL PROPERTIES
Boiling Point: 56.48 C
Melting Point: -94.6 C
Vapor Pressure: 400 mm Hg @ 39.5 C
Specific Gravity: 0.7972 @ 15 C
Odor threshold: 62 ppm - detection threshold; 130 ppm - recognition threshold
SOURC;ES OF CONTAMINATION
Bioeffluents
EXPOSURE LIMITS
OSHA PEL:TWA: 750 ppm (1800 mg/cu m) STEL: 1000 ppm (2400 mg/cu m)
NIOSH REL:TWA: 250 ppm (590 mg/cu m)
ACGIH TLV:TWA: 750 ppm (1780 mg/cu m) STEL:1000 ppm(2380 mg/cu m)
EPA Ambient Air Standard: Long term: 7 mg/cu m/ 24 hrs Short term: 24 mg/cu m/30 min
TOXICITY
Inhalation-man TDLo: 440 ug/cum/6 min
Inhalation-man LCLo: 10 mg/cu m/6 hrs
Inhalation-human TCLo: 500 ppm:EYE
Inhalation-human TCLo: 12000 ppm/4 hrs
Oral-human LDLo: 50 mg/kg
Oral-rat LD50: 9750 mg/kg
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I
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HEALTH HAZARDS
Moderately toxic by various routes. A skin and severe eye irritant. Human systemic effects by
inhala-
tion: changes in EEG, changes in carbohydrate metabolism, nasal effects, conjunctiva irritation,
respiratory system effects, nausea and vomiting, and muscle weakness. Narcotic in high concentra-
tion. A common air contaminant.
POSSIBLE MEANS OF REDUCING EXPOSURE
1. Clear all standing water indoors particularly if it is near the ventilation system;
2. Good operation & Maintenance of ventilation and humidification equipments;
3. Use strong biocide to disinfect certain areas when necessary.
MONITORING AND MEASUREMENT METHODS
NIOSH Method 1300, third edition
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Guide to Indoor Air Pollutants
ACROLEIN
MF: C3H4O MW: 56.07
IDENTIFICATION
Cas #: 107-02-8 NIOSH: AS1050000
SYNONYMS
Acquinite, acraldehyde, acrylaldehyde, acrylic aldehyde, awualine, biocide, crolean, ethylene al-
dehyde, magnacide H, 2-propenal, prop-2-en-1-al, 2-propen-1 -one, propylene aldehyde, slimicide.
APPEARANCE/ODOR
Colorless or yellowishliquid; disagreeable, choking odor.
CHEMICAUPHYSICAL PROPERTIES
Boiling Point: 52.5 C
Melting Point: -87.7 C
Vapor Pressure: 214 mm Hg @ 20 C
Specific Gravity: 0.841 @ 20 C/4 C
Odor threshold: 1.8 ppm - detection threshold (pungent)
SOURCES OF CONTAMINATION
Smoking, perfumes
EXPOSURE LIMITS
OSHA PEL:TWA: 0.1 ppm (0.25 mg/cu m) STEL: 0.3 ppm (0.8 mg/cu m)
NIOSH REL: none established
ACGIH TLV:TWA: 0.1 ppm (0.23 mg/cu m) STEL: 0.1 ppm(0.69 mg/cu m)
EPA Ambient Air Standard: Short term: 25 ug/cu m - ceiling
TOXICfTY
Inhalation-human LCLo: 5500 ppb
Inhalation-man LCLo: 1 ppm
Inhalation-human LCLo: 153 ppm/10 min
Inhalation-child TCLo: 300 ppb/2 hrs
Oral-rat LD50: 46 mg/kg
I
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HEALTH HAZARDS
Human poison by inhalation and intradermal route. Poison experimentally by most routes. An ex-
perimental carcinogen. Severe eye and skin irritant. Human systemic irritant and pulmonary system
ef-
fects by inhalation include: lacrimation, delayed hypersensitivity with multiple organ involvement
and
respiratory system damage. Human mutagenic data. Experimental reproductive effects.
POSSIBLE MEANS OF REDUCING EXPOSURE
Stop smoking and discourage others from smoking. Ask people who smoke to smoke outdoors.
Use alternative brands of perfumes that do not pollute indoor air.
MONITORING AND MEASUREMENT METHODS
NIOSH Method 2501, third edition.
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ALDRIN
MF: C12H86C16 MW: 364.93
I DENTI FICATION
Cas #: 309-00-2 NIOSH: 10 2100000
SYNONYMS
Aldrex, aldrex 30, aldrite, aldrosol, altox, compound 118, drinox, 1,2,3,4,10,10-hexachloro-
1,4,4a,5,88a-hexahydro-1,4,5,8-dimethanonaphthalene, octalene, seedrin, HHDN
APPEARANCE/ODOR
White crystaline odorless powder
CHEMICAL/PHYSICAL PROPERTIES
Boiling Point:
Melting Point: 104 C - 105 C
Vapor Pressure: 7.5 x 10-s
Specific Gravity: 1.57-1.63 @ 15.5 C/15.5 C
Odor threshold:
SOUR(3ES OF CONTAMINATION
Pesticide products used to kill household pests, and products used on lawns and gardens that drift
or
are tracked inside the house. Manufacturing and use has been discontinued in the U.S..
EXPO-SURE LIMITS
OSHA PEL: TWA: 0.25 mg/cu m - skin
NIOSH REL: reduce to lowest feasible level
ACGIH TLV: TWA: 0.25 ppm - skin
EPA Ambient Air Standards: none established
TOXICITY
Oral--human TDLo: 14 mg/kg: central nervous system
~
Skin-rat LD50: 39 mg/kg ~
04
~
~
~
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Page 2
HEALTH HAZARDS
Poison by ingestion, skin contact, intravenous, intraperitoneal and other routes. An experimental
tumorigen, neoplastigen, carcinogen and teratogen. Human systemic effects by ingestion: excite-
ment, tremors and nausea or vomiting. Experimental reproductive effects. Human mutagenic data.
Continued acute exposure causes liver damage.
POSSIBLE MEANS OF REDUCING EXPOSURE
1. Read the label and follow the directions.
2. Use in well vent'ilated areas.
3. Use alternative non-chemical methods of pest control.
4. If you decide to use a pest control company, choose one carefully.
5. Dispose of unwanted pesticides safely.
6. Keep exposure to moth repellents to a minimum.
7. Call the National Pesticide Telecommunications Network. The number is
MONITORING AND MEASUREMENT METHODS
NIOSH analytical method #5502, third edition
1-800-858-PEST.
44
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ALDEHYDES
MF: R*CHO MW:
IDENTIFICATION
Cas #: NIOSH:
SYNONYM
See individual aldehydes
APPEARANCE/ODOR
A class of chemicals with the general formula R*CHO, and characterized by an unsaturated carbonyl
group (C=0)
CHEMICAUPHYSICAL PROPERTIES
Boiling Point:
Melting Point:
Vapor Pressure:
Specific Gravity:
Odor threshold:
SOURCES OF CONTAMINATION
Exhaust of gasoline and diesel engines outdoors, tobacco smoke.
EXPOSURE LIMITS
OSHA PEL: None established
NIOSH REL: None established
ACGIH TLV: None established
EPA Ambient Air Standards: None established
TOXICITY
Inhalation-human LCLo: 5500 ppb
Inhalation-man LCLo: 1 ppm
Inhalation-human LCLo: 153 ppm/10 min
Inhalation-child TCLo: 300 ppb/2 hrs
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HEALTH HAZARDS
Aldehydes occur in nature and are gaseous by-products of incomplete combustion of wood and coal,
in exhaust from gasoline and diesel engines, industrial waste gases and fumes, tobacco smoke and
wood fires. Formaldehyde and acetaldehyde are carcinogens. Many of the aldehydes are mutagens.
All the aldehydes possess anesthetic properties, but this is obscured by their highly irritating
action on
the eyes and mucous membranes of the respiratory tract. The lower aldehydes act chiefly on the eyes
and tissues of the upper respiratory tract. The higher aldehydes tend to penetrate more deeply into
the respiratory system and may affect the lungs. Some higher aldehydes and also the aromatic af-
dehydes may exhibit much lower toxicity.
POSSIBLE MEANS OF REDUCING EXPOSURE
Check the ways of ventilation in your home or office. Try to reorganize the air
circulation/ventilation in
your home or offices in a way that intake of outdoor contaminated air is minimized. Do not smoke and
discourage others to smoke. Ask smokers to smoke outdoors.
MONlTORING AND MEASUREMENT METHODS
Aldehyde Screening, NIOSH analytical method 2539, third edition.
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Guide to Indoor Air Pollutants
ALKYL BENZENE SULFONATE
MF: C6H603S MW: 158.17
IDENTIPf ATI N
Cas #: 42615-29-2 NIOSH: DB 4370000
SYNONYMS
ABS; benzenesulfonic acid, alkyl derivatives; LAS; linear alkylbenzene sulfonate; lenear
alkylbenzene
suiphonate
APPEARANCE/ODOR
As ethyl ester - Colorless to slightly yellow, almost odorless liquid.
CHEMICAUPHYSICAL PROPERTIES
Boiling Point:
Melting Point: 43.44 C; 50-51 anhydrous
Vapor Pressure:
Specific Gravity:
Odor threshold:
SOURCES OF CONTAMINATION
Commercial cleaning products
EXPOSURE LIMITS
OSHA PEL: None established
NIOSH REL: None established
ACGIH TLV: None established
EPA Ambient Air Standards: None established
TOXICITY
Skin-mouse TDLo: 100 mg/kg (6-15 Day Pregnant)
Oral-rat LD50: 437 mg/kg
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HEALTH HAZARDS
Poison by intravenous route. Moderately toxic by ingestion and subcutaneous routes. An experimen-
tal teratogen. Other experimental reproductive effects. A skin irritant. When heated to decomposi-
tion, it emits SOx fumes.
POSSIBLE MEANS OF REDUCING EXPOSURE
1. Safe collection days for household hazardous waste should be organized;
2. Follow label instructions carefully before use;
3. Throw away partially full containers of old or unneeded household/office chemical products
safely;
4. Buy limited quantities of such products.
MONITORING AND MEASUREMENT METHODS'
No validated method.
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Guide to Indoor Air Pollutants
ALKYL ACRYL SODIUM SULFONATE
MF: MW:
IDENTIFI ATION
Cas #: NIOSH: AZ 8400000
SYNONYMS
D*40, witconate
APPEARANCE/ODOR
CHEMICAL/PHYSiCAL PROPERTIES
Boiling Point:
Melting Point:
Vapor Pressure:
Specific Gravity:
Odor threshold:
SOURCES OF CONTAMINATION
Commercial cleaning products
EXPOSURE LIMITS
OSHA PEL: None established
NIOSH REL: None established
ACGIH TLV: None established
EPA Ambient Air Standards: None established
TOXICITY
Oral-rat LD50: 2320 mg/kg
Oral-mouse LD50: 2010 mg/kg
Oral-rabbit LD50: 1730 mg/kg
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Page 2
HEALTH HAZARDS
Moderately toxic by ingestion. When heated to decomposition, emits toxic SOx fumes.
POSSIBLE MEANS OF REDUCING EXPOSURE
1. Safe collection days for household hazardous waste should be organized;
2. Follow label instructions carefully before use;
3. Throw away partially full containers of unneeded household/office chemical products safely;
4. Buy limited quantities of such products.
MONITORING AND MEASUREMENT METHODS,
No validated method found.
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Guide to Indoor Air Pollutants
AMMONIA
MF: H3N MW: 17.04
I DENTI FICATION
Cas #: 7664-41-7 NIOSH: BO 0875000
SYNONYMS
Ammonia anhydrous, ammonia gas, spirit of hartshorn
APPEARANCE/ODOR
Colorless gas, extremely pungent odor, liquefied by compression.
CHEMICAUPHYSICAL PROPERTIES
Boiling Point: -33.35 C
Melting Point: -77.7 C
Vapor Pressure: 10 atm @ 25.7 C
Specific Gravity: 0.771 g/liter @ 0 C, 0.817 g/liter @-79 C
Odor threshold: 17 ppm-detection threshold (pungent/irritating)
SOURC3ES OF CONTAMINATION
Microfilm machines, engineering drawing reproduction machines
EXPOSURE LIMITS
OSHA PEL: STEL: 35 ppm (27 mg/cu m)
NIOSH REL: STEL: 50 ppm (34.8 mg/cu m) - 5 minutes
ACGIH TLV: TWA: 25 ppm (17 mg/cu m) STEL: 35 ppm (24 mg/cu m)
EPA Ambient Air Standard: Long Term: 0.5 mg/cu m/year Short Term: 7 mg/cu m - ceiling level
TOXICITY
Inhalation-human LCLo: 30000 ppm/5 mins
Inhalation-human TCLo: 20 ppm
Oral-rat LD50: 350 mg/kg
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HEALTH HAZARDS
A human poison by an unspecified route. Poison experimentally by inhalation, ingestion and possibly
other routes. An eye, mucous membrane, and systemic irritant by inhalation. Mutagenic data. A com-
mon air contaminant.
POSSIBLE MEANS OF REDUCING EXPOSURE
1. To investigate general ventilation rates;
2. To investigate the possibility of local ventilation above the machine.
3. To locate the machine at a location where the pollution and exposure can be minimized; or possily
to confine the machine to specially partitioned rooms or compartments to prevent it from polluting
the
larger, general-use habitable space;
4. To find out if the manufacturer has introduced any modifications for reducing pollutant emission
of
the product; if no, search for a manufacturer that does.
5. Proper operation and maintenance of the machine.
MONITORING AND,MEASUREMENT METHODS
NIOSH Method 6701
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Guide to Indoor Air Pollutants
AMINES
MF: MW:
IDENTIFICATION
Cas #: NIOSH:
SYNONYMS
See individual compound(s).
APPEARANCE/ODOR
A large group of organic compounds containing nitrogen and considered as derived from ammonia
(NH3) by replacement of one or more hydrogen atoms by an organic radical. See also specific com-
pounds.
CHEMICAL/PHYSICAL PROPERTIES
Boiling Point:
Melting Point:
Vapor Pressure:
Specific Gravity:
Odor threshold:
SOURCES OF CONTAMINATION
Humidification equipments
EXPOSURE LIMITS
OSHA PEL: None established
NIOSH REL: None established
ACGIH TLV: None established
EPA Ambient Air Standards: None established
TOXf CIIY N
Q
tU
Variable toxicity, some are poison, some are only slightly toxic. Many are skin irritants and some
are ~~
sensitizers. C~`d
~
~
~
~
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HEALTH HAZARDS
Variable toxicity; some are poisons, some are only slightly toxic. Many are skin irritants and some
are
sensitizers. See also specific compounds.
POSSIBLE MEANS OF REDUCING EXPOSURE
Use other non-hazardous or less hazardous products to substitute amines.
MONITORING AND MEASUREMENT METHODS
NIOSH Method 2010, 2002, third edition
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Guide to Indoor Air Pollutants
AMMONIUM COMPOUNDS
MF: MW:
IDENTI FiCATiON
Cas #: NIOSH:
SYNONYMS
See individual compound(s)
APPEARANCE/ODOR
See individual compound(s)
CHEMICAUPHYSICAL PROPERTIES
Boiling Point:
Melting Point:
Vapor Pressure:
Specific Gravity:
Odor threshold:
S UR ES OF CONTAMINATION
Commercial cleaning products
EXPOSl1RE LIMITS
OSHA PEL: See individual compounds
NIOSH REL: See individual compounds
ACGIH TLV: See individual compounds
EPA Ambient Air Standard: See individual compounds
TOXICITY_
See individual compound(s)
HEALTH HAZARDS
See individual compound(s)
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Page 2
POSSIBLE MEANS OF REDUCING EXPOSURE
1. Safe collection days for household hazardous waste should be organized;
2. Follow label instructions carefully before use;
3. Throw away partially full containers of old or unneeded household/office chemical products
safely;
4. Buy limited quantities of such products.
MONITORING AND MEASUREMENT METHODS
See individuai ammonium compounds
I
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Guide to Indoor Air Pollutants
ASBESTOS
MF: MW:
IDENTIFICATION
Cas #: 1332-21-4 NIOSH: Cl 6475000
SYNONYMS
Amianthus, amphibole, asbestos fiber, fibrous grunerite, serpentine, amosite (OBS.)
APPEARANCE/ODOR
A group of fibrous hydrated mineral silicates.
CHEMICAUPHYSICAL PROPERTIES
Boiling Point: See each specific form of asbestos
Melting Point:
Vapor Pressure:
Specific Gravity:
Odor threshold:
SOURCES OF CONTAMINATION
Draperies, filters, stove mats, floor tile, spackling compound, furnaces (older), roofing, gaskets,
insula-
tion, acoustical materials, talcum powder, ironing board cover, hot mittens, hair dryers (old)
EXPOSURE LIMITS
OSHA PEL: See each specific form of asbestos
NIOSH REL: See each specific form of asbestos
ACGIH TLV: See each specific form of asbestos
EPA Ambient Air Standard: See each specific form of asbestos
T XICi'fY
Inhalation-human TCLo: 1.2 fibers/cc/19 years
HEALTH HAZARDS
A human carcinogen. An experimental tumorigen. Human pulmonary system effects by inhalation.
Usually at least 4 to 7 years of exposure are required before serious lung damage (fibrosis)
results. A
common air contaminant.
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POSSIBLE MEANS OF REDUCING EXPOSURE
Seek advice from an environmental engineering consultant. Control methods usually includes Opera-
tion & Maintenance Program and abatement.
MONITORING AND MEASUREMENT METHODS
See each specific form of asbestos
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Guide to Indoor Air Pollutants
ASBESTOS, ACTINOLITE
MF: Ca2(Mg1Fe)5(Si8O22)(OH)2 MW:
iDENTIIFICATION
Cas #: 77536-66-4 NIOSH: Cl 6476000
SYNONYMS I
Asbestos (ACGIH), actinolite asbestos
APPEA,RANCE/ODOR
Reticulated long prismatic crystals and fibers
CHEMICAUPHYSICAL PROPERTIES
Boiling Point:
Melting Point:
Vapor Pressure:
Specific Gravity:
Odor threshold:
SOURCES OF CONTAMINATION
Draperies, filters, stove mats, floor tile, spackling compound, furnaces (older), roofing, gaskets,
insula-
tion, acoustical materials, talcum powder, ironing board cover, hot mittens, hair dryers (old)
I EXP SURE LIMITS
OSHA PEL: 0.2 f/cc - carcinogen
NIOSH REL: 0.1 f/cc - carcinogen
ACGIH TLV: 2 f/cc - confirmed human carcinogen
EPA Ambient Air Standard:
I
TOXICIITY N
IC
CA
CJ't
HEALTH HAZARDS
A human carcinogen. An experimental tumorigen. Human pulmonary system effects by inhalation. ~
Usually at least 4 to 7 years of exposure are required before serious lung damage (fibrosis)
results. A ~
common air contaminant.
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POSSIBLE MEANS OF REDUCING EXPOSURE
Seek advice from an environmental engineering consultant. Control methods usually includes Opera-
tion & Maintenance Program and abatement.
MONITORING AND MEASUREMENT METHODS
NIOSH Method 7400, 7402, third edition
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Guide to Indoor Air Pollutants
ASBESTOS, AMOSITE
MF: Fe5Mg2(Si8022)(OH)2 MW:
I DENTI FlCATiON
Cas #: 12172-73-5 NIOSH: Cl 6477000
SYNONYMS
Asbestos (ACGIH), amosite asbestos, mysorite, NCI C60253A
APPEARANCE/ODOR
Amosite occurs as straight, brittle, coarser and generally long fibers that are light gray to pale
brown in
color. The more important features of amosite are its heat and corrosion resistance properties.
CHEM[CAUPHYSICAL PROPERTIES
Boiling Point:
Melting Point:
Vapor Pressure:
Specific Gravity :
Odor threshold:
SOURCES OF CONTAMINATION
Draperies, filters, stove mats, floor tile, spackling compound, furnaces, roofing, gaskets,
insulation,
acoustical materials, talcum powder, ironing board cover, hot mittens, hair dryers
EXPOSURE LIMITS
OSHA PEL: 0.2 f/cc - carcinogen
NIOSH REL: 0.1 f/cc - carcinogen
ACGIH TLV: 0.5 f/cc - confirmed human carcinogen
EPA Ambient Air Standard:
~
;
t
i
TOXICITY ~
~
Inhalation-rat TCLo: 11 mg/cu m/2 years-intermittent ~
*PA
~
~
~
a
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HEALTH HAZARDS
A human carcinogen. An,experimental carcinogen, neoplastigen and tumorigen by Inhalation and
most other routes. Mutagenic data. .
POSSIBLE MEANS OF REDUCING EXPOSURE
Seek an environmental engineering consultant. Control methods usually includes Operation & Main-
tenance Program and abatement.
MONITORING AND MEASUREMENT METHODS
NIOSH Method 7400, 7402, third edition
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ASBESTOS, ANTHOPHYLITE
MF: (Mg,Fe)7(Si8022)(OH)2 MW:
IDENTIFICATION ,
Cas #: 77536-67-5 NIOSH: CI 6478000
YN NYM
Asbestos (ACGIH), anthophylite, azbolen asbestos, ferroanthophyllite
APPEARANCEIODOR
A rare form of asbestos, characterized by white, brittle fibers. Its resistance to heat is good and
its
acid resistance properties are excellent.
CHEMICAUPHYSfCAL PROPERTIES
Boiling Point:
Melting Point:
Vapor Pressure:
Specific Gravity:
Odor threshold:
SOURCES OF CONTAMINATION
Draperies, filters, stove mats, floor tile, spackling compound, furnaces (older), roofing, gaskets,
insula-
tion, acoustical materials, talcum powder, ironing board cover, hot mittens, hair dryers (old)
EXPOSURE LIMITS
OSHA PEL: 0.2 f/cc - carcinogen
NIOSH REL: 0.1 f/cc - carcinogen
ACGIH TLV: 2 f/cc - confirmed human carcinogen
EPA Ambient Air Standard:
TOXICITY
Inhalation-rat TCLo: 11 mg/cu m/1 year-intermittent
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HEALTH HAZARDS
A human carcinogen. An experimental carcinogen, neoplastigen and tumorigen. Mutagenic data.
POSSIBLE MEANS OF REDUCING EXPOSURE
Seek advice from an environmental engineering consultant. Control methods usually includes Opera-
tion & Maintenance Program and abatement.
MONITORING AND MEASUREMENT METHODS
NIOSH Method 7400, 7402, third edition
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ASBESTOS, CHRYSOTILE
MF: Mg6(Si4010)(OH)8 MW: ;
1
IDENTIFICATION
Cas #: 12001-29-5 NIOSH: CI 6478500
SYNONYMS
Asbestos (ACGIH), 7-45 asbestos, asbestos white (DOT), avibest C, chrysotile asbestos, chrysotile
(DOT), metaxite, serpentine, serpentine chrysotile, sylidex, white asbestos, NCI C61223A
APPEARANCE/ODOR
Chrysotile is sufficiently distinctive in morphology to be identified by electron microscopy. Fibers
are
usually curved and occur in open bundles splitting into fibers and fibrils of 2,000 to 4,000 nm in
diameter. A single chrysotile fiberof 1% diameter may divide into 1,000 fibrils of the same length.
CHEMICAUPHYSICAL PROPERTIES
Boiling Point:
Melting Point:
Vapor Pressure:
Specific Gravity:
Odor threshold:
SOURCES OF CONTAMINATION
Draperies, filters, stove mats, floor tile, spackling compound, furnaces (older), roofing, gaskets,
insula-
tion, acoustical materials, talcum powder, ironing board cover, hot mittens, hair dryers (old)
EXPOSURE LIMITS
I
OSHA PEL: 0.2 f/cc - carcinogen
NIOSH REL: 0.1 f/cc - carcinogen
ACGIH TLV: 2 f/cc - confirmed human carcinogen
EPA Ambient Air Standard:
~
~
TOXICITY ~
~
Inhalation-man TCLo: 11 mppcf/cu m/1 year-continuous
Inhalation-human TCLo: 2.8 fb/cc/5 years r~+
~
~
~
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HEALTH HAZARDS
A human carcinogen by inhalation with tumors of the lung. An experimental carcinogen, neoplastigen
and tumorigen by inhalation and most other routes. Human mutagenic data. Poison by in-
traperitoneal route. Human systemic effects by inhalation: lung fibrosis, dyspnea and cough.
POSSIBLE MEANS OF REDUCING EXPOSURE
Seek advice from an environmental engineering consultant. Control methods usually includes Opera-
tion & Maintenance Program and abatement.
MONITORING AND MEASUREMENT METHODS
NIOSH Method 7400, 7402, third edition
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ASBESTOS, CROCIDOLITE
MF: MW:
1DENTYFiCATiON
Cas #: 12001-28-4 NIOSH: CI 6479000
SYNONYMS
Asbestos (ACGIH), amorphous crocidolite asbestos, blue asbestos (DOT), crocidolite asbestos,
crocidolite (DOT), fibrous crocidolite asbestos, NCI C09007
APPEARANCE/ODOR
It is commonly known as blue asbestos because of its distinctive color. This material, which has
straight, needle-like fibers, is the strongest of the asbestos minerals and is also acid resistant.
CHEMICAL/PHYSICAL PROPERTIES
Boiling Point:
Melting Point:
Vapor Pressure:
Specific Gravity:
Odor threshold:
SOURCES OF CONTAMINATION
Draperies, filters, stove mats, floor tile, spackling compound, furnaces (older), roofing, gaskets,
insula-
tion, acoustical materials, talcum powder, ironing board cover, hot mittens, hair dryers (old)
EXPOSURE LIMITS
OSHA PEL: 0.2 f/cc - carcinogen
NIOSH REL: 0.1 f/cc - carcinogen
ACGIH TLV: 0.2 f/cc - confirmed human carcinogen
EPA Ambient Air Standard:
~
~
TOXICITY ~
~11
Inhalation-rat TCLo: 11 mg/cu m/1 year - Intermittent
lnhalation-rat TC: 10 mg/cu m/8 hrs/52 weeks - continuousPage 2
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HEALTH HAZARDS
A human carcinogen. An experimental carcinogen, neoplastigen and tumorigen by inhalation and
most other routes. Human mutagenic data.
POSSIBLE MEANS OF REDUCING EXPOSURE
Seek advice from an environmental engineering consultant. Control methods usually includes Opera-
tion & Maintenance Program and abatement.
MONITORING AND MEASUREMENT METHODS
NIOSH Method 7400, 7402, third edition
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Guide to Indoor Air Pollutants
ASBESTOS, TREMOLITE
MF: Ca2Mg5(Si8022)(OH)2 MW:
IDENTIFICATION
Cas #: 77536-68-6 NIOSH: Cl 6560000
SYNONYM
Asbestos (ACGIH), fibrous tremolite, tremolite asbestos, NCI C08991
APPEARANCE/ODOR
Long, prismatic and fibrous aggregates.
CHEMICAUPHYSICAL PROPERTIES
Boiling Point:
Melting Point:
Vapor Pressure:
Specific Gravity:
Odor threshold:
S RCES OF CONTAMINATION
Draperies, filters, stove mats, floor tile, spackling compound, furnaces (older), roofing, gaskets,
insula-
tion, acoustical materials, talcum powder, ironing board cover, hot mittens, hair dryers (old)
EXPOSURE LIMITS
OSHA PEL: 0.2 f/cc - carcinogen
NIOSH REL: 0.1 f/cc - carcinogen
ACGIH TLV: 2 f/cc - confirmed human carcinogen
EPA Ambient Air Standard:
TOXICRTY
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HEALTH HAZARDS
A human carcinogen. An expetimental carcinogen and neoplastigen.
POSSIBLE MEANS OF REDUCING EXPOSURE
Seek advice from an environmental engineering consultant. Control methods usually includes Opera-
tion & Maintenance Program and abatement.
MONITORING AND MEASUREMENT METHODS
NIOSH Method 7400, 7402, third edition
I
1
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BENZALDEHYDE
MF: C7H60 MW:106.13
IDENTIFICATION
Cas #: 100-52-7 NIOSH: CU 4375000
SYNONYMS
Almond artificial essential oil, artificial almond oil, benzenecarbaldehyde, benzenecarbonal,
benzoic al-
dehyde,
dehyde,
NCI-C56133, benzene carbaldehyde
APPEARANCE/ODOR
Colorless to yellow mobile liquid, almond odor. Burning aromatic taste.
CHEMICAUPHYSICAL PROPERTIES
Boiling Point: 179 C
Melting Point: -56.5 C
Vapor Pressure: 1 mm Hg @ 26.2 C
Specific Gravity: 1.050 @ 15 C/4 C
Odor threshold: none established
SOURCES OF CONTAMINATION
Building maintenance materials including: paints, paint strippers, and other solvents; wood preserv-
atives, aerosol sprays, cleansers and disinfectants, moth repellents and air fresheners, stored
fuels
and automotive products, hobby supplies, dry cleaned clothing, etc..
EXPOSURE LIMITS
OSHA PEL: None established
NIOSH REL: None established
ACGIH TLV: None established
EPA Ambient Air Standard: None established
TOXICITY
Skin-rabbit 500 mg/24 hr Moderate
Oral-rat LD50: 1300 mg/kg
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HEALTH HAZARDS
Poison by ingestion and intraperitoneal routes. Moderately toxic by subcutaneous route. An allergen.
Acts as a feeble local anesthetic. Local contact may cause contact dermatitis. Causes central nerv-
ous system depression in small doses and convulsions in larger doses. A skin irritant.
POSSIBLE MEANS OF REDUCING EXPOSURE
1. Use household products according to manufacturer's directions.
2. Keep tightly closed and away from light. ,
3. Use outdoors or in well-ventilated places.
4. Throw away unused or little-used containers safely; buy in quantities that you will use soon.
MONITORING AND MEASUREMENT METHODS
Benzaldehyde and its impurities were separated by high-pressure liquid chromatography. Detection
limits of nitrobenzene were 6 mug, benzal chloride 0.788 mug, benzoic acid 0.1 mug (all in 1 mul
ben-
zaldehyde). [Block JH, Levine HL; Rapid and Sensitive HPLC technique for detecting impurities in
ben-
zaldehyde USP; J Chromatogr 166 (1): 313 (1978)]. Aldehydes (including benzaldehyde) were
detected in exhaust gas by high-performance liquid chromatography equipped with fluorescence
detector. [Swarin SJ, Lipari F; Determination of formaldehyde and other aldehydes by high-perfor-
mance liquid chromatography with fluorescence detection; J Liq Chromatogr 6 (3): 425-44 (1983)].
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BENZENE
MF: C6H6 MW: 78.12
1DENT(FICATION
Cas #: 71-43-2 NIOSH: CY 1400000
SYNONYMS
Benzol, benzolene, bicarburet of hydrogen, carbon oil, coal naphtha, cyclohexatriene, mineral naph-
tha, motor benzo(, nitration benzene, phene, phenyl hydride, pyrobenzole
APPEARANCE/ODOR
Clear, colorless, highly flammable liquid with characteristic odor.
CHEMICAUPHYSICAL PROPERTIES
Boiling Point: 80.093 C
Melting Point: 5.51 C
Vapor Pressure: 100 mm Hg @ 26.1 C
Specific Gravity: 0.8794 @ 20 C
Odor threshold: 61 ppm - detection threshold (aromatic/sweet/solven)
97 ppm - recognition threshold
SOURCES OF CONTAMINATION
Building maintenance materials Including: paints, paint strippers, and other solvents; wood preserv-
atives, aerosol sprays, cleansers and disinfectants, moth repellents and air fresheners, stored
fuels
and automotive products, hobby supplies, dry cleaned clothing, oil cloth, artificial leather.
EXPOSURE LIMITS
OSHA PEL: TWA: 1 ppm (3 mg/cu m) STEL: 5 ppm (15 mg/cu m)
NIOSH REL: TWA: 0.1 ppm(0.32 mg/cu m) STEL: 1 ppm (3.2 mg/cu m)
ACGIH TLV: TWA: 10 ppm (32 mg/cu m) - suspected human carcinogen
EPA Ambient Air Standard: None established
TOXICITY
Inhalation-human LCLo: 2 pph/5 min
Inhalation-human TCLo: 100 ppm
Inhalation-human TCLo: 210 ppm
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HEALTH HAZARDS
A human poison by inhalation. An experimental poison by skin contact, intraperitoneal, intravenous
and possibly other routes. Moderately toxic by ingestion and subcutaneous routes. A severe eye and
moderate skin irritant. Human systemic effects by inhalation and ingestion: euphoria, somnolence,
changes in REM sleep, changes in motor activity, nausea or vomiting, reduced number of blood
platelet, other unspecified blood effects, dermatitis and fever. A human carcinogen which produces
myeloid leukemia and lymphomas by inhalation. An experimental carcinogen, neoplastigen,
tumorigen and teratogen. Human mutagenic data. A narcotic. Exposures need to be reduced to 0.1
ppm before no toxic effects were observed. A common air pollutant.
POSSIBLE MEANS OF REDUCING EXPOSURE
1. Use household products according to manufacturer's directions.
2. Use outdoors or in well-ventilated places.
3. Throw away unused or little-used containers safely; buy in quantities that you will use soon.
MONITORING AND MEASUREMENT METHODS
NIOSH analytical method #3700, #1501, #S311, #217, third edition
OSHA Analytical method #12
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Guide to Indoor Air Pollutants
BENZO(a)PYRENE
MF: C20H12 MW: 252.32
IDENTIFiCATION
Cas #: 50-32-8 NIOSH: DJ 3675000
SYNONYMS
3,4-benzopyrene, 3,4-benzpyrene, 6,7-benzopyrene, benzo(def)chrysene, BAP, BP
APPEARANCE & ODOR
Pale yellow crystals; fluoresces yellow-green in ultraviolet light
CHEMICAUPHYSICAL PROPERTIES
Boiling Point: 310-312 C
Meiting Point: 179 - 179.3 C
Vapor Pressure: 1 mm Hg @ 68 F
Specific Gravity: 1.351
Odor threshold:
SOURCES OF CONTAMINATION
Combustion sources including gas ranges, dryers, water heaters, kerosene heaters, fireplaces and
wood stoves, gas stove, garages, outdoor sources, chimneys, furnaces
EXPOSURE_LIMITS
OSHA PEL: TWA: 0.2 ppm
NIC)SH REL: TWA: 0.1 ppm
ACGIH TLV: suspected human carcinogen
EPA Ambient Air Standard: None established
TOXICITY
Inhalation-human TCLo: 70 ngram/cu m/Y-C
Oral-mouse TDLo: 2310 mg/kg/11 W-C:ETA
Skin-mouse TD: 21 mg/kg/45 W-I:NEO
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HEALTH HAZARDS
May cause skin rash or eye irritation with redness and/or a burning sensation. Exposure to sunlight
in-
creases effects. Probable cancer causing agent. May cause skin changes such as thickening, darken-
ing and pimples. Bronchitis may result from repeated exposure. Smoking with exposure may cause
increased risk of lung cancer.
POSSIBLE MEANS OF REDUCING EXPOSURE 1. Keep gas appliance properly adjusted.
2. Consider purchasing vented gas space heaters and furnaces.
3. Use proper fuel in kerosene space heaters.
4. Install and use exhaust fan vented to outdoors over gas stoves.
5. Open flues when gas fire-places are in use.
6. Choose properly sized wood stoves that are certified to meet EPA emission standards. Make cer-
tain that doors on all wood stoves fit tightly.
7. Have a trained professional inspect, clean and tune-up`central heating system (furnaces, flues,
and
chimneys) annually. Repairany leaks properly.
8. Do not idle car inside garage.
MONITORING AND MEASUREMENT METHODS
NIOSH analytical method #5506 and #5515, third edition
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Guide to Indoor Air Pollutants
n-BUTYLACETATE
MF: C6H1202 MW: 116.18
IDENTIFICATION
Cas #: 123-86-4 NIOSH: AF 7350000
SYNONYMS
Acetic acid-n-butyl ester, butyl acetate, 1 -butyl acetate, butyl ethanoate
APPEARANCE/ODOR
Colorless liquid.
CHEMICAUPHYSICAL PROPERTIES
Boiling Point: 126 C
Melting Point:
Vapor Pressure: 15 mm Hg @, 25 C
Specific Gravity: 0.88 @ 20 Ci20 C
Odor threshold:
SOURCES OF CONTAMINATION
Building maintenance materials including: paints, paint strippers, and other solvents; wood preserv-
atives, aerosol sprays, cleansers and disinfectants, moth repellents and air fresheners, stored
fuels
and automotive products, hobby supplies, dry cleaned clothing, etc..
EXP SURE LIMITS
OSHA PEL:TWA: 200 ppm (590 mg/cu m) STEL: 300 ppm (885 mg/cu m)
NIOSH REL: None established
ACGIH TLV:TWA: 150 ppm(713 mg/cu m) . STEL: 200 ppm (950 mg/cu m)
EPA Ambient Air Standard: None established
TOXICITY
Inhalation-mouse LC50: 2 g/cu m/2 hr
Inhalation-human TCLo: 200 ppm
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HEALTH HAZARDS
Moderately toxic by intraperitoneal route. Mildly toxic by inhalation and ingestion. An experimental
teratogen. A skin and severe irritant. Human systemic effects by inhalation: conjunctiva irritation,
un-
specified nasal and respiratory system effects. A mild allergen. High concentrations are irritating
to
eyes and respiratory tract and cause narcosis.
POSSIBLE MEANS OF REDUCING EXPOSURE
1. Use household products according to manufacturer's directions.
2. Use outdoors or in well-ventilated places.
3. Throw away unused or little-used containers safely; buy in quantities that you will use soon.
MONITORING AND MEASUREMENT METHODS
NIOSH analytical method #1450, third edition
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Guide to Indoor Air Pollutants
BUTYRIC ACID
.
MF: C4H802 MW: 88.12
IDENTIFICATION
Cas #: 107-92-6 NIOSH: ES 5425000
. SYNONYMS
n-Butyric acid, butanoic acid, ethylacetic acid, 1-propanecarboxylic acid, propylformic acid
APPEARANCE/ODOR
Oily liquid; unpleasant, rancid odor.
CHEMICAUPHYSICAL PROPERTIES
Boiling Point: 163.5 C
Melting Point: -7.9 C
Vapor Pressure: 0.43 mm Hg @ 20 C
Specific Gravity: 0.9590 @ 20 C/20 C
Odor threshold:
SOURCES OF CONTAMINATION
Bioeffluents
EXPC)SURE LIMITS
OSHA PEL: None established
NIOSH REL: None established
ACGIH TLV: None established
EPA Ambient Air Standard: None established
TOXIClTY
Skin-rabbit LD50: 530 mg/kg
Eye-rabbit 250 ug open severe
Oral-rat LD50: 2940 mg/kg
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HEALTH HAZARDS
Moderately toxic by ingestion, skin contact, subcutaneous, intraperitoneal and intravenous routes.
Human mutagenic data. Severe skin and eye irritation. A corrosive material. Flammable when ex-
posed to heat or flame. May react with oxidizing materials.
POSSIBLE MEANS OF REDUCING EXPOSURE
Discard rancid butter.
MONITORING AND MEASUREMENT METHODS
OSHA Chemical Information Manual: IMIS 6709.
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Guide to Indoor Air Pollutants
CARBON
AF: C AW: 12.01
IDENTIFICATION
Cas #: 7440-44-0 NIOSH: FF 5250000
SYNONYMS
Black pearls, charcoal black, C.I. 77266, co(umbian carbon, purified charcoal
APPEARANCE/ODOR
Black crystals, powder or diamond form.
CHEMICAUPHYSICAL PROPERTIES
Boiling Point: approx. 4200 G
Melting Point: 3652-3697 C
Vapor Pressure: 1 mm Hg @ 3586 C
Specific Gravity: 1.8-2.1 (amorphous)
Odor threshold:
SOURCES OF CONTAMINATION
Photocopying machines
EXPOSURE LIMITS
OSHA PEL: None established
NIOSH REL: None established
ACGIH TLV: None established
EPA Ambient Air Standard: None established
TOXI QITY
Intravenous-mouse LD50: 440 mg/kg
HEALTH HAZARDS
Moderately toxic by intravenous route. Experimental reproductive effects. It can cause a dust
irrita-
tion, particularly to the eyes, and mucous membranes. Combustible when exposed to heat. Mildly
toxic by ingestion, inhalation, and skin contact.
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POSSIBLE MEANS OF REDUCING EXPOSURE
1. To investigate general ventilation rates;
2. To investigate the possibility of local ventilation above the machine.
3. To locate the machine at a location where the pollution and exposure can be minimized; or
possibly
to confine the machine to specially partitioned rooms or compartments to prevent it from polluting
the
larger, general-use habitable space;
4. To find out if the manufacturer has introduced any modifications for reducing pollutant emission
of
the product; if no, search for a manufacturer that does;
5. Proper operation and maintenance of the machine.
MONITORING AND MEASUREMENT METHODS
NIOSH analytical method #5000, third edition
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CARBON DIOXIDE
MF: C02 MW: 44.01
IDENTIFICATION
Cas #: 124-38-9 NIOSH: FF 6400000
SYNONYMS
Carbonic acid gas, carbonic anhydride, dry ice
APPEARANCE/ODOR
Colorless, odorless, noncombustible gas. Faint acid taste.
CHEMICALlPHYSICAL PROPERTIES
Boiling Point:
Melting Point: sublimes @ -78.5 C (-56.6 C @ 5.2 atm)
Vapor Pressure: 10.5 mm Hg @ -120 C
Specific Gravity: 1.527
Odor threshold:
SOURCES OF CONTAMINATION
Combustion sources including gas ranges, dryers, water heaters, kerosene heaters, fireplaces and
wood stoves, gas stove, garages, outdoor sources, chimneys, furnaces
EXPOSURE LIMITS
OSHA PEL: TWA: '10000 ppm (18000 mg/cu m) STEL: 30000 ppm (54000 mg/cu m)
N10SH REL: TWA: 10000 ppm (15000 mg/cu m) STEL: 30000 ppm (54000 mg/cu m)
ACGIH TLV: TWA: 5000 ppm (9000 mg/cu m) STEL: 30000 ppm (54000 mg/cu m)
EPA Ambient Air Standard:
TOXIClTY
Inhalation-human LCLo: 9 pph/5 mins
inhalation-human LCLo: 10 pph/1 min
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HEALTH HAZARDS
An asphyxiant. See discussion of simple asphyxiant under ARGON. An experimental teratogen.
Other experimental reproductive effects. Contact of carbon dioxide snow with the skin can cause
burns.
POSSIBLE MEANS OF REDUCING EXPOSURE
1. Keep gas appliance properly adjusted.
2. Consider purchasing vented gas space heaters and furnaces.
3. Use proper fuel in kerosene space heaters.
4. lnstall and use exhaust fan vented to outdoors over gas stoves.
5. Open flues when gas fire-places are in use.
6. Choose properly sized wood stoves that are certified to, meet EPA emission standards. Make cer-
tain that doors on all wood stoves fit tightly.
7. Have a trained professional inspect, clean and tune-up central heating system (furnaces, flues,
and
chimneys) annually. Repair any leaks properly.
8. Do not idle car inside garage.
MONITORING AND MEASUREMENT METHODS
NIOSH analytical method P&CAM S249, second edition
OSHA analytical method #172, second edition
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CARBON MONOXIDE
MF: CO MW: 28.01
IDENTIFICATION
Ca s#: 630-08-0 NIOSH: FG 3500000
SYNONYMS
Carbonic oxide; carbonic monoxide, cryogenic liquid (DOT); carbon oxide; exhaust gas; flue gas
APPEARANCE/ODOR
Colorless, odorless, flammable gas. Highly poisonous. -
CHEMICAUPHYSICAL PROPERTIES
Boiling Point: -191.3 C
Melting Point: -207 C
Vapor Pressure: 1 mm Hg @ 20 C
Specific Gravity: (gas) 1.250 g/L @ 0 C
Odor threshold: N/A
SOURCES OF CONTAMINATION
Combustion sources including gas ranges, dryers, water heaters, kerosene heaters, fireplaces and
wood stoves, gas stove, garages, outdoor sources, chimneys, furnaces .
EXPOSURE LIMITS
OSHA PEL: TWA: 35 ppm (40 mg/cu m) STEL: 200 ppm (229 mg/cu m) - ceiling
NIOSH REL: TWA: 35 ppm (40 mg/cu m) STEL: 200 ppm (229 mg/cu m)
ACGIH TLV: TWA: 50 ppm (57 mg/cu m) STEL: 400 ppm (458 mg/cu m)
EPA Ambient Air Standard: Short Term: 40 mg/cu m/i hr; Long Term: 10 mg/cu m/8 hrs
TOXICITY
Inhalation-man LCLo: 4000 ppm/30 mins
Inhalation-man TCLo: 650 ppm/45 mins
Inhalation-human LCLo: 5000 ppm/5 mins
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HEALTH HAZARDS
Mildly toxic by inhalation in humans. An experimental teratogen. Other experimental reproductive ef-
fects. Human systemic effects by inhalation: changes in psychophysiological tests and
methemoglobinemia-carboxhemoglobinemia. Can cause asphyxiations by preventing hemoglobin
from binding oxygen. After being removed from exposure, the half-life of its elimination from the
blood
is one hour. Chronic exposure effects can occur at lower concentrations. A common air contaminant.
Acute cases of poisoning resulting from brief exposures to high concentrations seldom result in any
permanent disability if recovery takes place. Chronic effects as the result of repeated exposure to
lower concentrations have been described. Glycosuria does occur, and heart irregularities have been
reported. Repeated' exposure to low concentration of the gas, up to 100 ppm in air, is generally
believed to cause no signs of poisoning or permanent damage. At low concentrations, fatigue in heal-
thy people and chest pain in people with heart disease. At higher concentrations, impaired vision
and
coordination; headaches; dizziness; confusion; nausea. Can cause flu-like symptoms that clear up
after leaving home.
POSSIBLE MEANS OF REDUCING EXPOSURE
1. Keep gas appliance properly adjusted.
2. Consider purchasing vented gas space heaters and furnaces.
3. Use proper fuel in kerosene space heaters.
4. Install and use exhaust fan vented to outdoors over gas stoves.
5. Open flues when gas fire-places are in use.
6. Choose properly sized wood stoves that are certified to meet EPA emission standards. Make cer-
tain that doors on all wood stoves fit tightly.
7. Have a trained professional inspect, clean and tune-up central heating system (furnaces, flues,
and
chimneys) annually. Repair any leaks properly.
8. Do not idle car inside garage.
MONITORING AND MEASUREMENT METHODS
NIOSH analytical method P&CAM 112, second edition
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Guide to Indoor Air Pollutants
CHLORDANE
MF: C10H6C18 MW: 409.76
IDENTIFICATION
Cas #: 57-74-9 NIOSH: PB 9800000
SYNONYMS
Aspon-chlordane, belt, CD 68, chlordan, chlorindan, chiorodane, chlortox, corodane, cortilan-neu,
dichiorochiordene, niran, octachior, octachlorodihydrodicyclopentadiene
APPEARANCE/ODOR
Colorless to amber, odorless, viscous liquid.
CHEMICAUPHYSICAL PROPERTIES
Boiling Point: 175 C
Melting Point:
Vapor Pressure:
Spe:cific Gravity: 1.57-1.63 @ 15.5 C/15.5 C
Odor threshold:
SOURCES OF CONTAMINATION
Pesticide products used to kill household pests, and products used on lawns and gardens that drift
or
are tracked inside the house. .
EXPOSURE LIMITS
OSHA PEL: TWA: 0.5 mg/cu m - skin
NIOSH REL:
ACGIH TLV: TWA: 0.5 mg/cu m - skin STEL: 2 mg/cu m - skin
EPA Ambient Air Standard:
ASHRAE Standard: 0.005 mg/cu rn/continuous
TOXICITY
Oral-human LDLo: 29 mg/kg
Inhalation-cat LC50: 100 mg/cu m/4 hr
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HEALTH HAZARDS
Poison to humans by ingestion and possibly other routes. An experimental poison by ingestion, in-
halation, intravenous and intraperitoneal routes. Moderately toxic by skin contact. A suspected
human carcinogen. An experimental carcinogen and teratogen. Other experimental reproductive ef-
fects. Human mutagenic data. A pesticide. it is no longer permitted for use as a termiticide in
homes.
POSSIBLE MEANS OF REDUCING EXPOSURE
1. Read the label and follow the directions. -
2. Use in well-ventilated areas.
3. Use alternative non-chemical methods of pest control.
4. If you decide to use a pest control company, choose one carefully.
5. Dispose of unwanted pesticides safely.
6. Keep exposure to moth repellents to a minimum.
7. Call the National Pesticide Telecommunications Network. The number is 1-800-858-PEST.
MONITORING AND MEASUREMENT METHODS
NIOSH analytical method #5510, third edition.
OSHA analytical method #67, second edition
88 Detail Associates, inc.

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CUMENE
MF: C9H12 MW: 120.21
IDENTIFICATION
Cas #: 98-82-8 NIOSH: GR 7350000
SYNONYMS
Benzene isopropyl, CUM, isopropyl benzene, isopropylbenzol, 2-phenylpropane, isopropyl benzol,
propane, z-phenyl
APPEARANCE/ODOR
Colorless liquid
HEMICAL/PHYSICAL PROPERTIES
Boiling Point: 152 C
Melting Point: -96.0 C
Vapor Pressure: 10 mm Hg @ 38.3 C
Specific Gravity: 0.864 @ 20 C/4 C
Odor threshold: 0.032 ppm - detection threshold (sharp)
0.047 ppm - recognition threshold
SOURCES OF CONTAMINATION
Building maintenance materials including: paints, paint strippers, and other solvents; wood preserv-
atives, aerosol sprays, cleansers and disinfectants, moth repellents and air fresheners, stored
fuels
and automotive products, hobby supplies, dry cleaned clothing, etc..
EXPOSURE LIMITS
OSHA PEL:TWA: 50 ppm (245 mg/cu m) - skin
NIOSH REL: TWA: 50 ppm (245 mg/cu m) - skin
ACGIH TLV:TWA: 50 ppm (246 mg/cu m) - skin
EPA Ambient Air Standard: None established
TOXICiTY
Inhalation-mouse LC50: 24700 mg/cu m/2 hr
Inhalation-human TCLo: 200 ppm
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HEALTH HAZARDS
Moderately toxic by ingestion. Mildly toxic by inhalation and skin contact. Human systemic effects
by
inhalation: an antipsychotic, unspecified changes in the sense of smell and respiratory system. An
eye
and skin irritant. Potential narcotic action. Central nervous system depressant.
POSSIBLE MEANS OF REDUCING EXPOSURE
1. Use household products according to manufacturer's directions.
2. Use outdoors or in well-ventilated places.
3. Throw away unused or little-used containers safely; buy in quantities that you will use soon.
MONITORING AND MEASUREMENT METHODS
NIOSH analytical method # 1501, third edition
OSHA analytical method #07, second edition
90 Detail Associates, Inc.

Guide to Indoor Air Pollutants
CYCLOHEXANE
MF: C6H12 MW: 84.18
IDEM"IFICATION
Cas #: 110-82-7 NIOSH: GU 6300000
SYNONYMS
Hexahydrobenzene, hexamethylene, hexanaphthene, RCRA waste number U056
APPEARANCE/ODOR
Colorless, flammable liquid; pungent odor.
CHEMICAL/PHYSICAL PROPERTIES
Boiling Point: 80.7 C
Melting Point: 6.5 C
Vapor Pressure: 100 mm Hg @ 60.8 C
Specific Gravity: 0.7791 @ 20 C/4 C
Odor threshold:780 ppm-detection threshold (pungent/solvent/oil)
SOURCES OF CONTAMINATION
Building maintenance materials including: paints, paint strippers, and other solvents; wood preserv-
atives, aerosol sprays, cleansers and disinfectants, moth repellents and air fresheners, stored
fuels
and automotive products, hobby supplies, dry cleaned clothing, etc..
EXPOSURE LIMITS
OSHA PEL:TWA: 300 ppm (1050 mg/cu m)
NIOSH REL: ceiling - 150 ppm
ACGIH TLV:TWA: 300 ppm (1030 mg/cu m)
EPA Ambient Air Standard:
TOXICITY
Oral-rat LD50: 29820 mg/kg
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HEALTH HAZARDS
Poison by intravenous route. Moderately toxic by ingestion. A systemic irritant by inhalation and
in-
gestion. A skin irritant. Mutagenic data.
POSSIBLE MEANS OF REDUCING EXPOSURE
1. Use household products according to manufacturer's directions.
2. Use outdoors or In well-ventilated places.
3.,Throw away unused or little-used containers safely; buy in quantities that you will use soon.
MONITORING AND MEASUREMENT METHODS
NIOSH analytical method # 1500, third edition
OSHA analytical method #07, second edition
92 Detail Associates, Inc.

Guide to Indoor Air Pollutants
CYCLOBiEXANOL
MF: C6H120 MW: 100.16
IDENTIFICATION
Cas #: 108-93-0 NIOSH: N/A
YNONYM
Adronal, anol, cyclohexyl alcohol, hexahydrophenol, hexalin, hydralin, hydrophenol,
hydroxycyclohexane, naxol
APPEARANCE/ODOR
Colorless needles or viscous liquid; hygroscopic, camphor-like odor.
CHEMICAUPHYSICAL PROPERTIES
Boiling Point: 161.5 C
Melting Point: 24 C
Vapor Pressure: 1 mm Hg @ 21 C
Specific Gravity: 0.9449 @ 25 C/4 C
Odor threshold: 0.16 ppm-detection threshold (camphorous)
SOURCES OF CONTAMINATION
Building maintenance materials including: paints, paint strippers, and other solvents; wood preserv-
atives, aerosol sprays, cleansers and disinfectants, moth repellents and air fresheners, stored
fuels
and automotive products, hobby supplies, dry cleaned clothing, etc..
EXPOSURE LiMiTS
OSHA PEL:TWA: 50 ppm (200 mg/cu m)
NIOSH REL: None established
ACGIH TLV:TWA: 50 ppm (206 mg/cu m)
EPA Ambient Air Standard: None established
TOXICITY
Eye-human 100 ppm
Oral-rat LD50: 2060 mg/kg
-I
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HEALTH HAZARDS
Poison by intravenous route. Moderately toxic by ingestion, subcutaneous and intramuscular routes.
Mildly toxic by skin contact. Human systemic effects by inhalation: conjunctiva irritation, and
changes
in the olfactory and respiratory systems. Has caused damage to kidneys, liver and blood vessels in
ex-
perimental animals. Experimental reproductive effects. Human mutagenic data. A severe eye irritant.
Narcotic-like action.
POSSIBLE MEANS OF REDUCING EXPOSURE
1. Use household products according to manufacturer's directions.
2. Use outdoors or in well-ventilated places.
3. Throw away unused or little-used containers safely; buy in quantities that you will use soon.
MONITORING AND MEASUREMENT METHODS
NIOSH analytical method # 1402, third edition
OSHA analytical method #07, second edition
N
II
94 Detail Associates, Inc.

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n-DECANE
MF: C10H22 MW: 142.29
IDENTIFICATION
Cas #: 124-18-5 NIOSH: HD 6550000
SYNONYMS
Decane
APPEARANCE/ODOR
Liquid.
CHEMICAUPHYSICAL PROPERTIES
Boiling Point: 174.1 C
Melting Point: -29.7 C
Vapor Pressure: 1 mm Hg @.16.5 C
Specific Gravity: 0.730 @ 20 C/4 C
Odor threshold:
SOURCES OF CONTAMINATION
Building maintenance materials including: paints, paint strippers, and other solvents; wood preserv-
atives, aerosol sprays, cleansers and disinfectants, moth repellents and air fresheners, stored
fuels
and automotive products, hobby supplies, dry cleaned clothing, etc..
EXPOSURE LIMITS
OSHA PEL: None established
NIOSH REL: None established
ACGIH TLV: None established
EPA Ambient Air Standard: None established
TOXICITY
Inhalation-mouse LC50: 72300 mg/cu m/2 hr
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HEALTH HAZARDS
An experimental tumorigen. A simple asphyxiant. Narcotic in high concentrations.
MEANS OF REDUCING EXPOSURE
1. Use household products according to manufacturer's directions.
2. Use outdoors or in well-ventilated places.
3. Throw away unused or little-used containers safely; buy in quantities that you will use soon.
MONITORING AND MEASUREMENT METHODS
OSHA Chemical Information Manual: IMISD166
ASTM D3416-88, Volume 11.03
96 Detail Associates, Inc.

Guide to Indoor Air Pollutants
DIEL.DRIN
MF: C12H8C16O MW: 380.90
IDENTIFICATION
Cas #: 60-57-1 NI OSH: 10 1750000
SYNONYM
Alvit, dieldrex, dieldrite, ent 16225, heod, hexachloroepoxyocta-hydroendo, exo-dimetha-nonaph-
thatene, illoxol, insecticide No. 497, octalox, panoram D-31, quintox
APPEARANCE/ODOR
White crystals, odorless
C;HEMICAUPHYSICAL PROPERTIES
Boiling Point:
Meiting Point: 150 C
Vapor Pressure:
S pecific G ravity (water =1) : 1.75
Odor threshold:
SOURCES OF CONTAMINATION
Pesticide products used to kill household pests, and products used on lawns and gardens that drift
or
are tracked inside the house.
EXPOSURE LIMITS
OSHA PEL: TWA: 0.25 ppm - skin
NIOSH REL: reduce to the lowest feasible level
ACGIH TLV: TWA: 0.25 ppm - skin
EPA Ambient Air Standard: None established
TOXICITY
Inhalation-cat LC50: 80 mg/cu m/4 hr
Inhalation-rat LC50: 43 mg/cu m/4 hr
I
I
I
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HEALTH HAZARDS
A human poison by ingestion and possibly other routes. Poison experimentally by inhalation, inges-
tion, skin contact, intravenous, intraperitoneal and possibly other routes. An experimental
carcinogen,
neoplastigen, tumorigen and teratogen. Experimental reproductive effects. Absorbed readily through
the skin and by other routes. It is a central nervous system stimulant. Human mutagenic data. An in-
secticide. Dieldrin is considerably more toxic than DDT by ingestion and skin contact.
MEANS OF REDUCING EXPOSURE
1. Read the label and follow the directions.
2. Use in weli-ventilated areas.
3. Use alternative non-chemical methods of pest control.
4. If you decide to use a pest control company, choose one carefully.
5. Dispose of unwanted pesticides safely.
6. Keep exposure to moth repellents to a minimum.
7. Call the National Pesticide Telecommunications Network. The number is 1-800-858-PEST.
MONITORING AND MEASUREMENT METHODS
NIOSH analytical method #5510, #S-283, third edition.
98 Detail Associates, Inc.

Guide to Indoor Air Pollutants
DIETHYL ETHANOLAMINE
MF: C6HISNO MW` 117.22
iDENTIFICATION
Cas #: 100-37-8 NIOSH: KK 5075000
SYNONYMS
n,n-diethylethanolamine, beta-diethylaminoethanol, n-diethylaminoethanol, 2-n-diethylaminoethanol,
2-
diethylaminoethanol, beta-diethlaminoethyl alcohol, n,n-diethyl-n-(beta-hydroxy-ethyl)amine, 2-
hydroxytriethylamine
APPEARANCE/ODOR
Colorless, hygroscopic liquid.
CHEMICAUPHYSICAL PROPERTIES
Boiling Point: 162 C
Melting Point:
Vapor Pressure: 1.4 mm @ 20 C
Specific Gravity: 0.88510 @ 20 C/20 C
Odor threshold: 0.011 ppm - detection threshold (amine/ammoniacal/sharp)
0.04 ppm - recognition threshold
SOURCES OF CONTAMINATION
Boiler additive
EXPOSURE LIMITS
OSHA PEL: TWA: 10 ppm (50 mg/cu m) - skin
NIOSH REL: None established
ACGIH TLV: TWA: 10 ppm (48 mg/cu m) - skin
EPA Ambient Air Standard: None established
~
QI ITY ~
~
Inhalation-human TCLo: 200 ppm ~
Inhalation-rat LCLo: 4500 mg/cu m/4H ~
Inhalation-mouse LC50: 5000 mg/cu m
~
~
~
~.
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HEALTH HAZARDS
Poison by intraperitoneal and intravenous routes. Moderately by ingestion, skin contact, sub-
cutaneous, intramuscular and possibly other routes. Human systemic effects by inhalation: nausea or
vomiting. A skin and severe eye skin irritant.
MEANS OF REDUCING EXPOSURE
Use non- or less-hazardous products to substitute Diethyl Ethanolamine.
MONITORING AND MEASUREMENT METHODS
I
NIOSH analytical methods #2007, third edition
OSHA Chemical Information Manual: 1MIS0920
100 Detail Associates, Inc.

Guide to Indoor Air Pollutants
DIETHYL RHTHALATE
MF: C12H1404 MW: 222.26
IDENTlFICATION
Cas #: 84-66-2 NIOSH: Tl 1050000
SYNONYMS
Anozol; 1,2-benzenedicarboxylic acid, diethyl ester; diethyl-o-phthalate; estol 1550; ethyl
phthalate,
neantine; palatinol A; phthalic acid, diethyl ester; phthalol; placidol E; solvanol
APPEARANCE/ODOR
Clear, colorless liquid
CHEMICAUPHYSICAL PROPERTIES
Boiling Point: 302 C
Melting Point: -40.5 C
Vapor Pressure:
Specific Gravity: 1.110 C
Odor threshold:
SOURCES OF CONTAMINATION
Building maintenance materials including: paints, paint strippers, and other solvents; wood preserv-
atives, aerosol sprays, cleansers and disinfectants, moth repellents and air fresheners, stored
fuels
and automotive products, hobby supplies, dry cleaned clothing, etc..
EXPOSURE LIMITS
OSHA PEL: TWA: 5 mg/cu m
NIOSH REL: None established
ACGIH TLV: TWA: 5 ppm
EPA Ambient Air Standard: None established
TOXICITY
Inhalation-human TCl_o: 1000 mg/cu m
I
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HEALTH HAZARDS
Poison by intravenous route. Moderately toxic by ingestion, subcutaneous and intraperitoneal routes.
Human systemic effects by inhalation: lachrymation, respiratory obstruction, and other unspecified
respiratory system effects. An eye irritant and systemic irritant by inhalation. An experimental
teratogen. Other reproductive effects. Narcotic in high concentrations.
MEANS OF REDUCING EXPOSURE
1. Use household products according to manufacturer's directions.
2: Use outdoors or in well-ventilated places.
3. Throw away unused or little-used containers safely; buy in quantities that you will use soon.
MONITORING AND MEASUREMENT METHODS
OSHA Chemical Information Manual:lMIS0933
102 Detail Associates, inc.

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DODECANE
MF: C12H26 MW: 181.36
IDENTIFICATION
Cas #: 2437-25-4 NIOSH: JR 2600000
SYNONYMS
Adakane 12, bihexyl, dihexyl, n-dodecan, duodecane
APPEARANCE/ODOR
CHEMICAL/PHYSICAL PROPERTIES
Boiling Point:
Melting Point:
Vapor Pressure:
Specific Gravity:
Odor threshold:
SOURCES OF CONTAMINATION
Building maintenance materials including: paints, paint strippers, and other solvents; wood preserv-
atives, aerosol sprays, cleansers and disinfectants, moth repellents and air fresheners, stored
fuels
and automotive products, hobby supplies, dry cleaned clothing, etc..
EXPOSURE LIMITS
OSHA PEL: None established :
NIOSH REL: None established
ACGIH TLV: None established
EPA Ambient Air Standard: None established
I
N
TOXICITY p
; IV
Skin-mouse TDLo: 11 g/kg/22 weeks ~
~
~
~
~
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HEALTH HAZARDS
An experimental tumorigen.
MEANS OF REDUCING EXPOSURE
1. Use household products according to manufacturer's directions.
2. Use outdoors or in well-ventilated places.
3. Throw away unused or little-used containers safely; buy in quantities that you will use soon.
MONITORING AND MEASUREMENT METHODS
OSHA Chemical Information Manual: IMIS D819
104 Detail Associates, inc.

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ETHYL ALCOHOL
MF: C2H60 MW: 46.08
IDENTIFICATION
Cas #: 64-17-5 NIOSH: KQ 6300000
SYNONYMS
Absolute ethanol, alcohol, alcohol, anhydrous, alcohol dehydrated, aigrain, anhydrol, cologne
spirit,
ethanol, ethanol 200 proof, ethanol solution (DOT), ethyl alcohol anhydrous, ethyl hydrate, ethyl
hydroxide, fermentation alcohol, grain alcohol, methylcarbinol, molasses alcohol, potato alcohol,
spirits of wine, spirit
APPEARANCE/ODOR
Clear, colorless, very mobile, fragrant liquid, burning taste.
CHEMICAUPHYSICAL PROPERTIES
Boiling Point: 78.32 C
Melting Point: 114.4 C
Vapor Pressure: 40 mm Hg @ 19 C
Specific Gravity: 0.7893 @ 20 C/4 C
Odor threshold: 180 ppm - detection threshold (sweet/alcohol)
100 ppm - recognition threshold
SOURCES OF CONTAMINATION
Bioeffluent
EXPOSURE LIMITS
OSHA PEL: TWA: 1000 ppm (1900 mg/cu m)
NIOSH REL: None established
ACGIH TLV: TWA: 1000 ppm (1880 mg/cu m)
EPA Ambient Air Standard: None established
TOXICITY
Inhalation-rat LC50: 20000 ppm/10 hrs
Inhalation-mouse LC50: 39 g/cu m/4 hrs
Oral-man TDLo: 1430 ug/kg
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HEALTH HAZARDS
Moderately toxic to humans by ingestion. Moderately toxic experimentally by intravenous and in-
traperitoneal routes. Mildly toxic by inhalation and skin contact. A experimental tumorigen and
teratogen. Human reproductive effects by ingestion, intravenous and intrauterine routes: changes in
female fertility index. Effects on newborn include: changes in apgar score, neonatal measures or ef-
fects and drug dependence. An eye and severe skin irritant. Exposure to concentrations over 1,000
ppm may cause headache, irritation of the eyes, nose and throat, and, if continued for an hour,
drowsi-
ness and lassitude, loss of appetite and inability to concentrate. Concentrations below 1,000 ppm
usually produce no signs of intoxication. There is no concrete evidence that repeated exposure to
ethanol vapor results in cirrhosis of the liver.
MEANS OF REDUCING EXPOSURE
Discard rancid butter.
MONITORING AND MEASUREMENT METHODS
NIOSH analytical methods #1400, third edition
OSHA analytical method #07, second edition
106 Detail Associates, Inc.

Guide to Indoor Air Pollutants
ETHYLEENZENE
MF: C8H10 MW: 106.18
1DENTIFICATION
Cas #: 100-41-4 NIOSH: DA 0700000
SYNONYMS
EB, ethylbenzol, phenylethane, NCI-C56393
APPEARANCE/ODOR
Colorless liquid, aromatic odor.
CHEMICAUPHYSICAL PROPERTIES
Boiling Point: 136.2 C
Melting Point: -95 C (-139 F)
Vapor Pressure: 10 mm Hg @ 25.9 C
Specific Gravity: 0.8669 @ 20 C/4 C
Odor threshold: none - oily/solvent
SOURCES OF CONTAMINATION
Building maintenance materials including: paints, paint strippers, and other solvents; wood preserv-
atives, aerosol sprays, cleansers and disinfectants, moth repellents and air fresheners, stored
fuels
and automotive products, hobby supplies, dry cleaned clothing, etc..
EXPOSURE LIMITS
OSHA PEL: TWA: 100 ppm (435 mg/cu m) STEL: 125 ppm (545 mg/cu m)
NIOSH REL: 50 ppm - ceiling
ACGIH TLV: TWA: 100 ppm (434 mg/cu m) STEL: 125 ppm (543 mg/cu m)
EPA Ambient Air Standard: None established
TOXICITY
Inhalation-human TCLo: 100 ppm/8 hr
Inhalation-rat LCLo: 50 g/cu m/2 hr
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HEALTH HAZARDS
Moderately toxic by ingestion and intraperitoneal route. Mildly toxic by inhalation and skin
contact.
An experimental teratogen. Human systemic effects by inhalation: eye, sleep and pulmonary changes.
An eye and skin irritant. Human mutagenic data. The liquid is an irritant to the skin and mucous
membranes. A concentration of 0.1 % of the vapor in air is an irritant to human eyes, and a
concentra-
tion of 0.2% is extremely irritating at first, then causes dizziness, irritation of the nose and
throat and a
sense of constriction in the chest. No data are available regarding the effect of chronic exposure.
MEANS OF REDUCING EXPOSURE
1. Use household products according to manufacturer's directions.
2. Use outdoors or in well-ventilated places.
3. Throw away unused or little-used containers safely; buy in quantities that you will use soon.
MONITORING AND MEASUREMENT METHODS
NIOSH analytical method #1501, third edition.
OSHA analytical method #07, second edition
I
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1-ETHYL-2-M ETHYLB E NZ E N E
MF: C9H12 MW: 120.21
IDENTIFICATION
Cas #: 611-14-3 NIOSH: XT 2500000
SYNC)NYMS
2-ethyltoluene, o-ethyl methylbenzene, o-ethyltoluene, o-methylethylbenzene
APPEARANCE/ODOR
CHEMICAL/PHYSICAL PROPERTIES
Boiling Point: 164.1 C
Melting Point:
Vapor Pressure:
Specific Gravity: 0.88
Odor threshold:
SOURCES OF CONTAMINATION
Building maintenance materials including: paints, paint strippers, and other solvents; wood preserv-
atives, aerosol sprays, cleansers and disinfectants, moth repellents and air fresheners, stored
fuels
and automotive products, hobby supplies, dry cleaned clothing, etc..
EXP SURE LIMITS
OSHA PEL: None established
NIOSH REL: None established
ACGIH TLV: None established
EPA Ambient Air Standard: None established
TOXICITY
Inhalation-mouse LC50: 54 g/cu m/4 hr
Inhalation-cat LC50: 50 glkg/2 hr
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HEALTH HAZARDS
Mildly toxic by ingestion and inhalation.
MEANS OF REDUCING EXPOSURE
1. Use household products according to manufacturer's directions.
2. Use outdoors or in well-ventilated places.
3. Throw away unused or little-used containers safely; buy in quantities that you will use soon.
MONITORING AND MEASUREMENT METHODS
OSHA Chemical Information Manual: IMIS E109
i
110 Detail Associates, Inc.

Guide to Indoor Air Pollutants
1-ETHYL-4-INI ETHYLBENZEN E
MF: C9H12 MW: 120.21
IDENTIFICATION
Cas #: 611-14-3 NIOSH: XT 2500000
SYNONYMS
p-ethyltoluene, p-ethyl methylbenzene, 4-ethyltoluene, p-methylethylbenzene, 4-methylethylbenzene
APPEARANCE/ODOR
CHEMlCAL/PHYSICAL PROPERTIES
BoiEing Point: 162.2 C
Melting Point: -62.4 C
Vapor Pressure:
Specific Gravity:
Odor threshold:
SOURCES OF CONTAMINATION
Building maintenance materials including: paints, paint strippers, and other solvents; wood preserv-
atives, aerosol sprays, cleansers and disinfectants, moth repellents and air fresheners, stored
fuels
and automotive products, hobby supplies, dry cleaned clothing, etc..
EXPOSURE LIMITS
OSHA PEL: None established
NIOSH REL: None established
ACGIH TLV: None established
EPA Ambient Air Standard: None established
TOXICITY N
O
Oral-rat LDLo: 5000 mg/kg N
~
~11
d
~
W
0
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HEALTH HAZARDS
Mildly toxic by ingestion.
MEANS OF REDUCING_EXPOS_U_RE
1. Use household products according to manufacturer's directions.
2. Use outdoors or in well-ventilated places.
3. Throw away unused or little-used containers safely; buy in quantities that you will use soon.
MONITORING AND MEASUREMENT METHODS
OSHA Chemical Information Manual: E215
112 Detail Associates, Inc.

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FORMALDEHYDE
MF: CH2O MW: 30.03
IDENTIFICATION
Cas #: 50-00-0 NIOSH: LP 8925000
SYNONYMS
Fannoform, formalin, formalin 40, formalith, formic aldehyde, formol, fyde, hoch, ivalon, karsan,
lysoform, methanal, methyl aldehyde, methylene glycol, methylene oxide, morbocid, oxomethane,
oxymethylene, paraform, superiysoform
APPEARANCE/ODOR
Clear, water-white, very slightly acid gas or liquid; pungent odor.
CHEMICAUPHYSICAL PROPERTIES
Boiling Point: -3 F
Melting Point: -92 C
Vapor Pressure: N/A
Specific Gravity: 1.0
Odor threshold: none - pungent
SOURCES OF CONTAMINATION
Particle board, urea-formaldehyde insulation, pressed wood, plywood resins, hardwood paneling, car-
peting, upholstery, paper towels, disinfectants, carpet shampoos, toothpaste, smoking, grocery bags,
waxed paper, facial towels, shampoo, cosmetics, medicines
EXPOSURE LIMITS
OSHA PEL: TWA: 1 ppm STEL: 2 ppm
NIOSH REL: TWA: 0.016 ppm STEL: 0.1 ppm
ACGIH TLV: TWA: 1 ppm (1.2'mg/cu m) STEL: 2 ppm (2.5 mg/cu m) - suspected human carcinogen N
EPA Ambient Air Standard: 120 ug/cu m/30 min O
WHO Guidelines: 0.1 mg/cu m/30 min
ASf-iRAE Standard: 0.1 mg/cu m - ceiling N~
TOXICITY
Inhalation-human TCLo: 17 mg/cu m/30 min
Inhalation-man TCLo: 300 ug/cu m
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HEALTH HAZARDS
Human poison by ingestion. Experimental poison by ingestion, skin contact, inhalation, intravenous,
intraperitoneal and subcutaneous routes. A suspected human carcinogen. An experimental car-
cinogen, tumorigen and teratogen. Human systemic effects by inhalation: lacrimation, olfactory chan-
ges, aggression and pulmonary changes. Experimental reproductive effects. Human mutagenic data.
A human skin and eye irritant. Frequent or prolonged exposure can cause hypersensitivity leading to
contact dermatitis. An air concentration of 20 ppm is quickly irritating to eyes. A fungicide. A
com-
mon air contaminant.
MEANS OF REDUCING EXPOSURE
1. Use "exterior grade" pressed wood products (lower-emitting because they contain phenol resins,
not urea resins).
2. Use air conditioning and dehumidifiers to maintain moderate temperature and reduce humidity
levels.
3. Increase ventilation, particularly after bringing new sources of formaldehyde into the home.
MONITORING AND MEASUREMENT METHODS
NIOSH analytical methods #2542, 3501, 3500, third edition
OSHA analytical methods #52 or 102
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HEPTACHLOR
MF: C10HSC17 MW: 373.3
IDENTIFICATION
Cas #: 76-44-8 NIOSH: PC 0700000
SYNONYMS
Agroceres, 3-chiorochiordene, drinox, 3,4,5,6,7,8,8-heptachiorodicyclopentadiene, heptagram, hep-
tarnul, rhodiachlor, velsicol 104, 4,7-methousindene, 1,4,5,6,7,8,8-heptachloro-3a,
4,7,7a-tetrahydro,
dicyllopentodiene
APPEARANCE/ODOR
Crystals.
CHEMICAUPHYSICAL PROPERTIES
Boiling Point:
Melting Point: 96 C
Vapor Pressure: 3 x 4-4 mm Hg @ 25 C
Specific Gravity: 1.57 @ 9 C
Odor threshold:
SOURCES OF CONTAMINATION
Pesticide products used to kill household pests, and products used on lawns and gardens that drift
or
are tracked inside the house.
EXPOSURE LIMITS
- OSHA PEL: TWA: 0.5 mg/cu m - skin
NIOSH REL: ceiling - 0.25 mg/cu m
ACGIH TLV: TWA: 0.5 mg/cu m - skin
EPA Ambient Air Standard: None established
TOXICITY
Oralrat LD50: 40 mg/cu m
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HEALTH HAZARDS
A poison by ingestion, skin contact, intraperitoneal, intravenous, and possibly other routes. An ex-
perimental carcinogen. Human mutagenic data. Acute exposure and chronic doses have caused liver
damage. Acute symptoms include tremors, convulsions, kidney damage, respiratory collapse and
death.
MEANS OF REDUCING EXPOSURE
1. Read the label and follow the directions.
2. Use in well-ventilated areas.
3. Use alternative non-chemical methods of pest control.
4. If you decide to use a pest control company, choose one carefully.
5. Dispose of unwanted pesticides safely.
6. Keep exposure to moth repellents to a minimum.
7. Call the National Pesticide Telecommunications Network. The number is 1-800-858-PEST.
MONITORING AND MEASUREMENT METHODS
NIOSH analytical method P&CAM S287, volume 5, second edition.
OSHA Chemical Information Manual: IMIS1369
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n-HEPTANE
MF: C7H16 MW: 100.23
IDENTIFiCATION
Cas #: 142-82-5 NIOSH: MI 7700000
SYNONYM
Dipropyl methane, gettysolve-C, heptane, heptyl hydride, skellysolve C
APPEARANCE/ODOR
Volatile, flammable, colorless liquid
CHENIICAUPHYSICAL PROPERTIES
Boiling Point: 98.52 C
Melting Point: 90.61 C
Vapor Pressure: 40 mm Hg @ 22.3 C
Specific Gravity: 0.684 @ 20 C/4 C
Odor threshold: 230 ppm - detection threshold (gasoline)
330 ppm - recognition threshold
S URCES OF CONTAMINATION
Building maintenance materials including: paints, paint strippers, and other solvents; wood preserv-
atives, aerosol sprays, cleansers and disinfectants, moth repellents and air fresheners, stored
fuels
and automotive products, hobby supplies, dry cleaned clothing, etc..
EXPOSURE LIMITS
OSHA PEL:IINA: 400 ppm (1600 mg/cu m) STEL: 500 ppm (2000 mg/cu m)
NIOSH REL: TWA: 85 ppm (350 mg/cu m) STEL: 440 ppm (1800 mg/cu m)
ACGIH TLV: TWA: 400 ppm (1640 mg/cu m) STEL: 500 ppm (2050 mg/cu m)
EPA, Ambient Air Standard: None established
TOXICITY
Inhalation-human TCLo: 1000 ppm/6 min:central nervous system
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HEALTH HAZARDS
Poison by intravenous route. Human systemic effects by inhalation: hallucinations. Narcotic in high
concentration.
MEANS OF REDUCING EXPOSURE
1. Use household products according to manufacturer's directions.
2. Use outdoors or in well-ventilated places.
3. Throw away unused or little-used containers safely; buy in quantities that you will use soon.
MONITORING AND MEASUREMENT METHODS
NIOSH analytical method #1500, third edition
OSHA analytical method #07, second edition
118 Detail Associates, Inc.

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HYDROGEN CYANIDE
MF: CHN MW: 27.03
IDENTIFICATION
Cas #: 74-90-8 NIOSH: MW 6825000
SYNONYMS
Hydrocyanic acid, aero liquid HCN, cyclon, cyclone B, fluohydric acid gas, HCN, hydrofluoric acid
gas, zaclon discoids, RCRA waste # P063
APPEARANCE & ODOR
Colorless gas or liquid, characteristic odor
CHEMICAUPHYSICAL PROPERTIES
Boiling Point: 25.6 C
Melting Point: -13.4 C
Vapor Pressure:
Specific Gravity: 0.941 (gas); 0.687 (liquid)
Odor threshold:
SOURCES OF CONTAMINATION
Combustion sources including gas ranges, dryers, water heaters, kerosene heaters, fireplaces and
wood stoves, gas stove, garages, outdoor sources, chimneys, furnaces
EXPOSURE LIMITS
OSHA PEL: TWA: 0.2 ppm STEL: 4.7 ppm
NIOSH REL: TWA: 0.1 ppm STEL: 4.7 ppm Ceiling: 5 ppm
ACGIH TLV: suspected human carcinogen
EPA Ambient Air Standard: None established
TOXICITY
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HEALTH HAZARDS
An experimental tumorigen and teratogen. Other experimental reproductive effects. A suspected car-
cinogen. Human mutagenic data. When heated to decomposition, it emits acrid smoke and irritating
fumes. Headache, vertigo, nausea and vomitting may occur of less concentration.
MEANS OF REDUCING EXPOSURE
1. Keep gas appliance properly adjusted.
2. Consider purchasing vented gas space heaters and furnaces.
3. Use proper fuel in kerosene space heaters.
4. Install and use exhaust fan vented to outdoors over gas stoves.
5. Open flues when gas fire-places are in use.
6. Choose properly sized wood stoves that are certified to meet EPA emission standards. Make cer-
tain that doors on all wood stoves fit tightly.
7. Have a trained professional inspect, clean and tune-up central heating system (furnaces, flues,
and
chimneys) annually. Repair any leaks properly.
8. Do not idle car inside garage.
MONITORING AND MEASUREMENT METHODS
NIOSH analytical method #6010, third edition
OSHA analytical method #120, second edition
120 Detail Associates, Inc.

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KEROSENE
MF: MW:
IDENTIFICATION
Cas #: 8008-20-6 NIOSH: OA 5500000
SYNONYMS
Coal oil, kerosine, petroleum distillate
APPEi%RANCE/ODOR
A pale yellow to water-white, mobile, oily liquid. Characteristic, not altogether disagreeable odor.
CHEMICAUPHYSICAL PROPERTIES
Boiling Point: 175 C - 325 C
Melting Point:
Vapor Pressure:
Specific Gravity: 0.80
Odor threshold:
S URDES OF CONTAMINATION
Commercial cleaning products
EXPOSURE LIMITS
OSHA PEL: None established
NIOSH REL: TWA: 100 ppm
ACGiH TLV: None established
EPA Ambient Air Standard: None established
TOXICITY
Oral-man TDLo: 3570 mg/kg
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HEALTH HAZARDS
Poison by intravenous and intratracheal routes. Moderately toxic to_humans by an unspecified route.
Moderately toxic to animals by ingestion. Aspiration of vomitus can cause serious pneumonitis, par-
ticularly in young children. Human systemic effects by ingestion and intravenous routes: somnolence,
hallucinations and distorted perceptions, coughing, nausea or vomiting, and fever.
MEANS OF REDUCING EXPOSURE
1. Use according to manufacturer's directions.
2. Use outdoors or in well-ventilated places.
3. Throw away unused or little-used containers safely; buy in quantities that you will use soon.
MONITORING AND MEASUREMENT METHODS
NIOSH analytical method #1550
OSHA Chemical Information Manual 1MIS K107
122 Detail Associates, Inc.

Guide to Indoor Air Pollutants
LEAD
MF: Pb MW: 207.19
I DENTI FICATION
Cas #: 7439-92-1 NIOSH: OF 7525000
SYNONYMS
C.I. 77575, C.I. Pigment Metal 4, glover, lead flake, lead S2, omaha, omaha & grant, SI, SO
APPEARANCE/ODQR
Bluish-gray, soft metal
CHEM[CAUPHYSiCAL PROPERTIES
Boiling Point: 1740 C
Melting Point: 327.43 C
Vapor Pressure: 1 mm Hg @ 973 C
Specific Gravity: 11.34 @ 20 C/4 C
Odor threshold:
SOURCES OF CONTAMINATION
Automobile exhaust, sanding or open-flame burning of lead-based paint, activities involving lead
solder, outdoor sources
EXPOSURE LIMITS
OSHA PEL: 'NVA: 0.05 ppm
NIOSH REL: TWA: ppm
ACGIH TLV: TWA: 0.15 ppm
EPA, Ambient Air Standard: 1.5 ug/cu m/3 month
WHO Guidelines: 0.5-1 ug/cu m/annual
ASHRAE Standard: 1.5 ug/cu m/24 hr
TY
TOXIC]
Inhalation-human TCLo: 10 ug/cu m
Inhalation-rat TCLo: 10 mg/cu m/24 hr
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HEALTH HAZARDS
Impaired mental and physical development in both fetuses and young children. Decreased coordina-
tion and mental abilities; damage to kidneys and nervous system, and red blood cells. May increase
high blood pressure.
MEANS OF REDUCING EXPOSURE
1. If you suspect that paint you are removing may contain lead, hat it tested.
2. Cover lead-based paint with wallpaper or other building material. Replace moldings and other
woodwork or have them removed and chemically treated,offsite.
3. Use well-ventilated areas for hobby and house maintenance activities involving lead. Consider
using "no-lead" solder.
4. If lead exposure is suspected, consult your health department about appropriate removal and
clean-
up procedures and have your blood lead levels tested.
5. Have your drinking water tested for lead.
MONITORING AND MEASUREMENT METHODS
NIOSH analytical method #7082,7300,8003,8005
OSHA analytical method #121 or #125, second edition
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LIMONENE
MF: C10H16 MW: 136.26
IDENTIFICATION
Cas #: 138-86-3 NIOSH: OS 8100000
SYNONYMS
p-mentha-1,8-diene, acintene DP, acintene DP dipentene, cajeputene, cinene, dipanol, dipentene,
inac-
tive limonene, Kautschin, dl-limonene, i,8(9)-p-menthadiene, 1-methyl-4-isopropenyl-cyclohexene,
nesol, unitene
APPEARANCE/ODOR
Liquid, pleasant lemon-like odor.
CHEMICAUPHYSiCAL PROPERTIES
Boiling Point: 175.5-176.5 C
Melting Point: -96.9 C
Vapor Pressure:
Specific Gravity: 0.842 @ 20 C/4 C
Odor threshold: None established
SOURCES OF CONTAMINATION
Building maintenance materials including: paints, paint strippers, and other solvents; wood preserv-
atives, aerosol sprays, cleansers and disinfectants, moth repellents and air fresheners, stored
fuels
and automotive products, hobby supplies, dry cleaned clothing, etc.:
EXPOSURE LIMITS
OSHA PEL: None established
NIOSH REL: None established
ACGIH TLV: None established
EPA Ambient Air Standard: None established
TOXICITY
Skin-rabbit 500 mg/24 hr moderate
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HEALTH HAZARDS
A skin irritant.
MEANS OF REDUCING EXPOSURE
1. Use household products according to manufacturer's directions.
2. Use outdoors or in well-ventilated places.
3. Throw away unused or little-used containers safely; buy in quantities that you will use soon.
MONITORING AND MEASUREMENT METHODS
OSHA Chemical Information Manual: IMIS L129
126 Detail Associates, Inc.

Guide to Indoor Air Pollutants
MAN-MADE MINERAL FIBERS
MF: MW:
IDENTIFICATION
Cas #: NIOSH:
SYNONYMS
APPEARANCE/ODOR
CHEMICAUPHYSICAL PROPERTIES
Boiling Point:
Melting Point:
Vapor Pressure:
Specific Gravity:
Odor threshold:
SOURCES OF CONTAMINATION
Fiberglass insulation, mineral wool insulation
EXPOSURE LIMITS
OSHA PEL: None established
NIOSH REL: None established
ACGIH TLV: None established
EPA Ambient Air Standard: None established
TOXICITY
HEALTH HAZARDS
I
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MEANS OF REDUCING EXPOSURE
Obtain help from an environmental engineering consultant. Control method usually include operation
& maintenance and abatement.
MONITORING AND MEASUREMENT METHODS
N
I
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MENTHONE
MF: ClOH180 MW: 154.26
IDENTIFICATION
Cas #: 89-80-5 NIOSH: OS 9542200
SYNCINYMS
p-rnenthone, trans-menthone, trans-5-methyl-2-(1-methyl-ethyl)-cyclohexanone, 2-isopropyl-5-methyl
cyclohexanone
APPEARANCE/ODOR
Liquid
CHEMICAUPHYSICAL PROPERTIES
Boiling Point: 210.5 C
Melting Point:
Vapor Pressure:
Specific Gravity: 0.991
Odor threshold:
SOURCES OF CONTAMINATION
Building maintenance materials including: paints, paint strippers, and other solvents; wood preserv-
atives, aerosol sprays, cleansers and disinfectants, moth repellents and air fresheners, stored
fuels
and automotive products, hobby supplies, dry cleaned clothing, etc..
EXPOSURE LIMITS
OSHA PEL: None established
NIOSH REL: None established
ACGfH TLV: None established
EPA Ambient Air Standard: None established
TOXICITY
Oral-mouse LD50: 3100 mg/kg
Skin-rabbit 500 mg/24 hr mild
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HEALTH HAZARDS
Moderately toxic by ingestion, intraperitoneal, and subcutaneous routes. Mutagenic data.
MEANS OF REDUCING EXPOSURE
1. Use household products according to manufacturer's directions.
2. Use outdoors or in well-ventilated places.
3. Throw away unused or little-used containers safely; buy in quantities that you will use soon.
MONITORING AND MEASUREMENT METHODS
Photometric detection can be important parameter in optimizing separation of essential oil con-
stituents. [Strack D et al; Reversed Phase High Performance Liquid Chromatography of Essential Oils;
Z Naturforsch, C: Biosci 35C(9-10) 675 (1980)].
Two methods were used to detect menthone in essential oils, silylation followed by gas chromatog-
raphy-mass spectrometry & extraction with Girard D Reagent followed by gas chromatography. [Bic-
chi C, Frattini C; J Chromatogr 190(2) 471 (1980)].
130 Detail Associates, Inc.

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MESITYLENE
MF: C9H12 MW: 120.21
IDENTIFICATION
Cas #: 108-67-8 NIOSH: OX 6825000
SYNONYMS
Fleet-X, sym-trimethylbenzene, 1,3,5-trimethylbenzene, trimethylbenzol
APPEARANCE/ODOR
A liquid, peculiar odor
CHEMICAL/PHYSICAL PROPERTIES
Boiling Point: 164.7 C
Melting Point: -44.8 C
Vapor Pressure:
Specific Gravity: 0.8637 @ 20 C/4 C
Odor threshold:
SOURCES OF CONTAMINATION.
Building maintenance materials including: paints, paint strippers, and other solvents; wood preserv-
atives, aerosol sprays, cleansers and disinfectants, moth repellents and air fresheners, stored
fuels
and automotive products, hobby supplies, dry cleaned clothing, etc..
EXPOSURE LIMITS
OSHA PEL: TWA: 25 ppm
NIOSH REL: None established
ACGIH TLV: None established
EPA Ambient Air Standards: None established
TOXICITY
inhalation-human TCLo: 10 ppm
Inhalation-rat LC50: 24 mg/cu m/4 hrPage 2
I
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HEALTH HAZARDS
Poison by inhalation. Moderately toxic by intraperitoneai route. Human systemic effects by inhala-
tion: sensory changes involving peripheral nerves, somnolence (general depressed activity), and
struc-
tural or function change in trachea or bronchi. Reports of leukopenia and thrombocytopenia in
experimental animals. Mutagenic data.
MEANS OF REDUCING EXPOSURE
1. Use household products according to manufacturer's directions.
2. Use outdoors or in well-ventilated places.
3. Throw away unused or little-used containers safely; buy in quantities that you will use soon.
MONITORING AND MEASUREMENT METHODS
OSHA Chemical Information Manual: IMIS 2505
i
132 Detail Associates, Inc.

Guide to Indoor Air PotIutants
METHYL ACRYLATE
MF: C4H602 MW: 86.10
IDENTIFICATION
Cas #: 96-33-3 NIOSH: AT 2800000
SYNONYM
Acrylic acid methyl ester, curithane 103, methoxycarbonylethylene, methyl propenate, methyl
propenoate, methyl-2-propenoate, propenoic acid methyl ester, 2-propenoic acid methyl ester
APPEARANCE/ODOR
Colorless liquid; acrid odor.
CHEMICAUPHYSiCAL PROPERTIES
Boiling Point: 70 C @ 608 mm
Melting Point: -76.5 C
Vapor Pressure: 100 mm Hg @ 28 C
Specific Gravity: 0.9561 @ 20 C/4 C
Odor threshold: none - detection threshold (plastic/sharp/airplane glue)
SOURCES OF CONTAMINATION
Signature machine
EXPOSURE LIMITS
OSHA PEL: TWA: 10 ppm (35 mg/cu m) - skin
NIOSH REL: Ceiling: 5 ppm
ACGIH TLV: TWA: 10 ppm (35 mg/cu m) - skin
EPA Ambient Air Standards: None established
TOXICITY
Inhalation-human TCLo: 75 ppm
Inhalation-rat LC50: 1350 ppm/4 hr
Inhalation-mouse LCLo: 9300 mg/cu mPage 2
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HEALTH HAZARDS
1
I
Poison by ingestion and intraperitoneal routes. Moderately toxic by skin contact. Mildly toxic by
in-
halation. A suspected carcinogen. Human systemic effects by inhalation: olfaction effects, eye
effects
and respiratory effects. A skin and eye irritant. Mutagenic data. Chronic exposure has produced in-
juryto lungs, liver and kidneys in experimental animals.
MEANS OF REDUCING EXPOSURE
1. To investigate general ventilation rates;
2. To investigate the possibility of local ventilation above the machine.
3. To locate the machine at a location where the pollution and exposure can be minimized; or
possibly
to confine the machine to specially partitioned rooms or compartments to prevent it from polluting
the
larger, general-use habitable space;
4. To find out if the manufacturer has introduced any modifications for reducing pollutant emission
of
the product; if no, search for a manufacturer that does;
5. To properly operate and maintain the machine.
MONITORING AND MEASUREMENT METHODS
NIOSH analytical method 538, Volume 2, second edition .
OSHA analytical method #07, second edition
134 Detail Associates, Inc.

Guide to Indoor Air Pollutants
METHYL ALCOHOL
MF: CH40 MW: 32.05
1 DENTI FICATION
Cas #: 67-56-1 NIOSH: PC 1400000
YN NYM
Methanol, carbinol, colonial spirit, columbian spirits (DOT), methyl hydroxidemethylol,
monohydroxymethane, pyroxylic spirit, wood alcohol, wood naphtha, wood spirit
APPEARANCE/ODOR
Clear, colorless, very mobile liquid. Slight alcoholic odor when pure; crude material may have a
repul-
sive pungent odor.
CHEMICAUPHYSICAL PROPERTIES
Boiling Point: 64.8 C (108 F)
Melting Point: -97.8 C (-144 F) (freezing point)
Vapor Pressure: 100 mm Hg @ 21.2 C
Specific Gravity: 0.7915 @ 20 C/4 C
Odor threshold: 160 ppm - detection threshold (sour/sweet)
690 ppm - recognition threshold
SO RCES OF CONTAMINATION
Spirit duplication machine, bioeffluent
EXPOSURE LIMITS
OSHA PEL: TWA: 200 ppm (260 mg/cu m) STEL: 250 ppm (310 mg/cu m)
NIOSH REL: TWA: 200 ppm (262 mg/cu m) STEL: 800 ppm (1048 mg/cu m)
ACGIH TLV: TWA: 200 ppm (262 mg/cu m) STEL: 250 ppm (328 mg/cu m)
ASHRAE Standard: 14 mg/cu m/24 hr; 42 mg/cu m/30 min
TOXICITY
Inhalation-human TCLo: 86000 mg/cu m
Inhalation-human LDLo: 143 mg/cu m
Inhalation-human TCLo: 300 ppm
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HEALTH HAZARDS
A human poison by ingestion. Poison experimentally by skin contact. Moderately toxic experimental-
ly by intravenous and intraperitoneal routes. Mildly toxic by inhalation. Human systemic effects by
in-
gestion and inhalation: optic nerve neuropathy, visual field changes, lacrimation, headache, cough,
dyspnea, other respiratory effects, nausea or vomiting. An experimental teratogen. Experimental
reproductive effects. An eye and skin irritant. Human mutagenic data. A narcotic. A common air con-
taminant.
MEANS OF REDUCING EXPOSURE
1. To investigate general ventilation rates;
2. To investigate the possibility of local ventilation above the machine.
3. To locate the machine at a location where the pollution and exposure can be minimized; or
possibly
to confine the machine to specially partitioned rooms or compartments to prevent it from polluting
the
larger, general-use habitable space;
4. To find out if the manufacturer has introduced any modifications for reducing pollutant emission
of
the product; if no, search for a manufacturer that does;
5. To properly operate and maintain the machine.
6. Clear all standing water indoors particularly if it is near the ventilation system;
7. Good operation & Maintenance of ventilation and humidification equipments;
8. Use strong biocide to disinfect certain areas when necessary.
MONITORING AND MEASUREMENT METHODS
NIOSH analytical method #2000, third edition
OSHA Chemical Information Manual: IMIS 1660
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METHYLENE CHLORIDE
MF: CH2C12 MW: 84.93
1DENTIFICATION
Cas #: 75-09-2 NIOSH: PA 8050000
SYNONYMS
Methane dichioride, aerothene mm, DCM, dichioromethane, freon 30, methylene bichloride, methylene
dichloride, solmethine, NCI-C50102, RCRA waste number U080
APPEARANCE/ODOR
Colorless, volatile liquid
CHEMICAUPHYSICAL PROPERTIES
Boiling Point: 39.8 C
Melting Point: -96.7 C (freezing point)
Vapor Pressure: 380 mm Hg @ 22 C
Specific Gravity: 1.326 @ 20 C/4 C
Odor threshold: 160 ppm - detection threshold (sweet)
230 ppm - recognition threshold
SOURCES OF CONTAMINATION
Building maintenance materials including: paints, paint strippers, and other solvents; wood preserv-
atives, aerosol sprays, cleansers and disinfectants, moth repellents and air fresheners, stored
fuels
and automotive products, hobby supplies, dry cleaned clothing, etc..
EXPOSURE LIMITS
OSHA, PEL: TWA: 500 ppm STEL: 1000 ppm (2000 mg/cu m) - ceiling
NIOSH REL: reduce to lowest feasible level
ACGIH TLV: TWA: 50 ppm - suspected human carcinogen STEL: 174 mg/cu m- suspected
human carcinogen
EPA Ambient Air Standard:
WHO Guidelines: 3 mg/cu m/24 hr
ASHRAE Standards: 20 mg/cu m/24 hr; 50 mg/cu m/annual
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T XICITY
I
Inhalation-human TCLo: 500 ppm/8 hr:central nervous system
Inhalation-human TCLo: 500 ppm/1 year
Inhalation-rat LC50: 88000 mg/cu m/30 min
HEALTH HAZARDS
Poison by intravenous route. Moderately toxic by ingestion, subcutaneous and intraperitoneal route.
Mildly toxic by inhalation. An experimental carcinogen and tumorigen. Human systemic effects by in-
gestion and inhalation: paresthesia, somnolence, altered sleep time, convulsions, euphoria, and
change in cardiac rate. An experimental teratogen. Experimental reproductive effects. An eye and
severe skin irritant. Human mutagenic data.
MEANS OF REDUCING EXPOSURE
1. Use household products according to manufacturer's directions.
2. Use outdoors or in well-ventilated places.
3. Throw away unused or little-used containers safely; buy in quantities that you will use soon.
MONITORING AND MEASUREMENT METHODS
NIOSH analytical method #1005, third edition.
OSHA analytical method ##59 or #07, second edition.
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1-METHYLNAPHTHALENE
MF: C11H10 MW: 142.21
IDENTIFICATION
Cas #: 90-12-0 NIOSH: QJ 9630000
SYNONYMS
alpha-methylnaphthalene
APPEARANCE/ODOR
Colorless liquid
CHEMICAUPHYSICAL PROPERTIES
Boiling Point: 244.6 C
Melting Point: -22 C
Vapor Pressure:
Specific Gravity: 1.0202 0 20 Cl4 C
Odor threshold:
SOURCES OF CONTAMINATlON
Building maintenance materials including: paints, paint strippers, and other solvents; wood preserv-
atives, aerosol sprays, cleansers and disinfectants, moth repellents and air fresheners, stored
fuels
and automotive products, hobby supplies, dry cleaned clothing, etc..
EXPOSURE LIMITS
OSHA PEL: None established
NIOSH REL: None established
ACGIH TLV: None established
EPA Ambient Air Standard: None established
TOXICITY
Oral-rat LD50: 1840 mg/kg
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HEALTH HAZARDS
Moderately toxic by ingestion. Mutagenic data.
MEANS OF REDUCING EXPOSURE
1. Use household products according to manufacturer's directions.
2. Use outdoors or in well-ventilated places.
3. Throw away unused or little-used containers safely; buy in quantities that you will use soon.
MONITORING AND MEASUREMENT METHODS
OSHA Chemical Information Manual: IMIS 1779
1.40 Detail Associates, Inc.

Guide to Indoor Air Pollutants
2-METHYLNAPHTHALENE
MF: C11H10 MW: 142.21
1 DENTI F(CATION
Cas #: 91-57-6 NIOSH: QJ 9635000
SYN NYMS
beta-methylnaphthaiene
APPEARANCE/ODOR
Solid
CHEMiCAUPHYSICAL PROPERTIES
Boiling Point: 241.1 C
Melting Point: 34.58 C
Vapor Pressure:
Specific Gravity: 1.0058 @ 20 C/4 C
Odor threshold:
SOURCES OF CONTAMINATION
Building maintenance materials including: paints, paint strippers, and other solvents; wood preserv-
atives, aerosol sprays, cleansers and disinfectants, moth repellents and air fresheners, stored
fuels
and automotive products, hobby supplies, dry cleaned clothing, etc..
EXPOSURE LIMITS
OSHA PEL: None established
NIOSH REL: None established
ACGIH TLV: None established
EPA, Ambient Air Standard: None established
TOXICITY
Oral-rat LD50: 1630 mg/kg
Intraperitoneal-mouse LDLo: 1000 mg/kgPage 2
HEALT'H HAZARDS
Moderately toxic by ingestion and intraperitoneal routes. Mutagenic data.
I
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MEANS OF REDUCING EXPOSURE
1. Use household products according to manufacturer's directions.
2. Use outdoors or in well-ventilated places.
3. Throw away unused or little-used containers safely; buy in quantities that you will use soon.
MONITORING AND MEASUREMENT METHODS
OSHA Chemical Information Manual: IMIS 1779
142 Detail Associ.ates,'Inc.

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NAPHTHA
MF: MW:
IDENTIFICATION
Cas #: 8030-30-6 NIOSH: DE 3030000
SYNONYMS
Naphtha, coal tar; ansco H-J; Amsco H-SB; benzin B70; coal tar naphtha distillate; 160 degree
benzol;
hi-flash naphtha; naphtha, petroleum benzin; petroleum naphtha, super VMP
APPEARANCE/ODOR
Dark straw-colored to colorless liquid.
CHEMICAUPHYSICAL PROPERTIES
Boiling Point: 149 C - 216 C
Melting Point:
Vapor Pressure:
Specific Gravity: 0.862-0.892
Odor threshold:
SOURCES OF CONTAMINATION
Commercial cleaning products
EXPOSURE LIMITS
OSHA PEL: TWA: 100 ppm (400 mg/cu m)
NIOSH REL: TWA: 100 ppm (400 mg/cu m)
ACGIH TLV: TWA: None established
EPA Ambient Air Standard: None established
TOXICITY
Inhalation-human LCLo: 3 pph/5 min
Inhalation-rat LCLo: 1600 ppm/f hr
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HEALTH HAZARDS
I
I
Mildly toxic by inhalation. Can cause unconsciousness which may go to coma, stentorious breathing,
and bluish tint to the skin. Recovery follows removal from exposure. In mild form, intoxication
resembles drunkenness. On a chronic basis, no true poisoning; sometimes headache, lack of ap-
petite, dizziness, sleeplessness, indigestion, and nausea. A common air contaminant.
MEANS OF REDUCING EXPOSURE
1. Use according to manufacturer's directions.
2. Use outdoors or in well-ventilated places.
3. Throw away unused or little-used containers safely; buy'in quantities that you will use soon.
MONITORING AND MEASUREMENT METHODS
NIOSH analytical method #1550, third edition
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NAPHTHALENE
MF: C10H8 MW:128.18
IDENTIFICATION
Cas #: 91-20-3 NIOSH: QJ 0175000
SYNONYMS
Camphor tar, mighty 150, moth balls, moth flakes, naphthalin (DOT), naphthaline, naphthene, NCI-
C52904, RCRA waste number U165, tar comphor, white tar
APPEARANCE/ODOR
Aromatic odor; white, crystalline, volatile flakes.
CHEMICAUPHYSICAL PROPERTIES
BoiGing Point: 217.9 C
Melting Point: 80.1 C
Vapor Pressure: 1 mm Hg @ 52.6 C
Specific Gravity: 1.162
Odor threshold: 0.038 ppm - detection threshold (tar/creosote/mothballs)
SOURCES OF CONTAMINATION
Building maintenance materials including: paints, paint strippers, and other solvents; wood preserv-
atives, aerosol sprays, cleansers and disinfectants,.moth repellents and air fresheners, stored
fuels
and automotive products, hobby supplies, dry cleaned clothing, etc..
EXPOSURE LIMITS
OSHA PEL: TWA: 10 ppm (50 mg/cu m) STEL: 15 ppm (75 mg/cu m)
NIOSH REL: None established
ACGIH TLV:TWA: 10 ppm (52 mg/cu m) STEL: 15 ppm (79 mg/cu m)
EPA Ambient Air Standard: None established
TOXICITY
Oral-rat LD50: 1780 mg/kg
Skin-rabbit 495 mg open mild
Eye-rabbit 100 mg mild
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HEALTH HAZARDS
Human poison by ingestion and possibly other routes. Experimental poison by ingestion, intravenous
and intraperitoneal routes. Moderately toxic by subcutaneous route. An experimental tumorigen. Ex-
perimentai reproductive effects. Mutagenic data. An eye and skin Irritant. Can cause nausea,
headache, diaphoresis, hematuria, fever, anemia, liver damage, vomiting, convulsions, and coma.
Poison may occur by ingestion of large doses, inhalation, or skin absorption.
MEANS OF REDUCING EXPOSURE
1. Use household products according to manufacturer's directions.
2. Use outdoors or in well-ventilated places.
3. Throw away unused or little-used containers safeiy; buy in quantities that you will use soon.
MONITORING AND MEASUREMENT METHODS
NIOSH analytical method #1501, third edition
OSHA analytical method #35, second edition
L
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NIC®TtIvE
MF: C10H14N2 MW: 162.26
IDEN-f1FICAT(ON
Cas #: 54-11-5 NIOSH: QS 5250000
SYNONYMS
black leaf, fumetobac, 1 -methyl-2-(3-pyridyl)pyrrolidine, nicocide, nico-dust, nico fume, ortho n-4
dust,
tendust, dl-tetrahydronicotyrine, XL all insecticide, etc.
APPEARANCE/ODOR
An alkaloid from tobacco. In its pure state, a colorless and almost odorless oil; sharp burning
taste.
CHEMICAUPHYSICAL PROPERTIES
Boiling Point: 247.3 C
Melting Point: -79 C
Vapor Pressure:l mm Hg @ 61.8 C
Specific Gravity: 1.0092 @ 20 C
Odor threshold:
S URCES OF CONTAMINATION
Tobacco smoke
EXPOSURE LIMITS
OSHA PEL: TWA: 0.5 mg/cu m - skin
NIOSH REL: Ceiling: 0.25 mg/cu m
ACGIH TLV: TWA: 0.5 ppm - skin
EPA Ambient Air Standard: None established
TOXICITY
Oral-rat LD50: 50'mg/kg
Skin-rat LD50: 140 mg/kg
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HEALTH HAZARDS
I
I
A deadly human poison by unspecified route. Experimental poison by ingestion, skin contact, in-
traperitoneal, subcutaneous, intravenous, intramuscular, parenteral, intratracheal and intraduodenal
routes. Human systemic effects by rectal route: hallucinations, distorted perceptions, nausea or
vomit-
ing. An experimental teratogen. Experimental reproductive effects. "Nicotinism", poisoning by
nicotine, is characterized by stimulation and subsequent depression of the central and autonomic
nerv-
ous systems. Death can result from respiratory paralysis. Mutagenic data.
MEANS OF REDUCING EXPOSURE
1. Stop smoking and discourage others from smoking.
2. Ask smokers to smoke outdoors.
MONITORING AND MEASUREMENT METHODS
NIOSH analytical method S293, Volume 3, second edition
OSHA Chemical Information Manual: 1MIS 1855
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NITROGEN DIOXIDE
MF: N02 MW: 46.01
IDENTIFI ATf N
Cas #: 10102-44-0 NIOSH: OW 9800000
SYNONYMS
Nitrito; nitrogen peroxide, liquid (DOT); RCRA waste number P078
APPEARANCE/ODOR
Colorless solid to yellow liquid; irritating odor
CHEMICAL/PHYSICAL PROPERTIES
Boiling Point: 21 C (red-brown gas with decomposition)
Melting Point: -9.3 C (yellow liquid)
Vapor Pressure: 400 mm Hg @ 80 C
Specific Gravity: 1.491 @ 0 C
Odor threshold: none - bleach
SOURCES OF CONTAMINATION
Combustion sources including gas ranges, dryers, water heaters, kerosene heaters, fireplaces and
wood stoves, gas stove, garages, outdoor sources, chimneys, furnaces
EXPOSURE LIMITS
OSHA PEL: STEL: 1 ppm (1.8 mg/cu m)
NIOSH REL: TWA: 10 ppm STEL: 1 ppm (1.8 mg/cu m)
ACGIH TLV: TWA: 3 ppm (5.6 mg/cu m) STEL: 5 ppm (9.4 mg/cu m)
EPA Ambient Air Standard: Long Term: 1.5 ug/cu m/3 months
TOXICITY
Inhalation-man TCLo: 6200 ppb/10 mins
Inhalation-man TCLo: 90 ppm/40 mins
Inhalation-human LCLo: 200 ppm/1 min
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HEALTH HAZARDS
I
L
poison by Inhalation. Moderately toxic to humans by inhalation. An experimental
teratogen. Human systemic effects by inhalation: pulmonary vascular resistance changes, cough,
dyspnea and other pulmonary changes. Experimental reproductive effects. Eye, nose and throat irrita-
tion; may cause impaired lung function and increased respiratory infections in young children.
MEANS OF REDUCING EXPOSURE
1. Keep gas appliance properly adjusted.
2. Consider purchasing vented gas space heaters and furnaces.
3. Use proper fuel in kerosene space heaters.
4. Install and use exhaust fan vented to outdoors over gas stoves.
5. Open flues when gas fire-places are in use.
6. Choose properly sized wood stoves that are certified to meet EPA emission standards. Make cer-
tain that doors on all wood stoves fit tightly.
7. Have a trained professional inspect, clean and tune-up central heating system (furnaces, flues,
and
chimneys) annually. Repair any leaks properly.
8. Do not idle car inside garage.
MONITORING AND MEASUREMENT METHODS
NIOSH analytical method #6700, #320, #11, third edition
OSHA analytical method #109, #182, second edition
150
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NONANE
MF: C9H20 MW: 128.29
IDENTIFICATION
Cas #: 111-84-2 NIOSH: RA 6115000
SYNONYMS
Shellsol 140, n-nonane
APPEARANCEiODQR
Colorless liquid
CHEMICAUPHYSICAL PROPERTIES
Boiling Point: 150.7 C
Melting Point: -53.7 C
Vapor Pressure: 10 mm Hg @ 38.0 C
Specific Gravity: 0.718 @ 20 C/4 C
Odor threshold: nonane - gasoline
SQURIDES OF CONTAMINATION
Building maintenance materials including: paints, paint strippers, and other solvents; wood preserv-
atives, aerosol sprays, cleansers and disinfectants, moth repelfents and air fresheners, stored
fuels
and automotive products, hobby supplies, dry cleaned clothing, etc..
EXPOSURE LIMITS
OSHA PEL: TWA: 200 ppm (1050 mg/cu m)
NIOSH REL: None established
ACGIH TLV:TWA: 200 ppm (1050 mg/cu m)
EPA Ambient Air Standard: None established
TOXICITY
Inhalation-rat LC50: 3200 ppm/4 hr
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HEALTH HAZARDS
Poison by intravenous route. Mildly toxic by inhalation. Irritating to respiratory tract. Narcotic
in high
concentrations.
MEANS OF REDUCING EXPOSURE
1. Use household products according to manufacturer's directions.
2. Use outdoors or in well-ventilated places.
3. Throw away unused or little-used containers safely; buy in quantities that you will use soon.
MONITORING AND MEASUREMENT METHODS
OSHA Chemical Information Manual: IMIS N807
I
L
r
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n-OCTANE
MF: C8H18 MW: 114.26
IDEMf IFICATION
Cas #: 111-65-9 NIOSH: RG 8400000
SYNONYMS
Octane
APPEARANCE/ODOR
Clear liquid.
CHEMICAUPHYSICAL PROPERTIES
Boiling Point: 125.8 C
Melting Point: -56.7 C
Vapor Pressure: 10 mm Hg @ 19.2 C
Specific Gravity: 0.7036 @ 20 CJ4 C
Odor threshold: 150 ppm - detection threshold (gasoline, oil)
240 ppm - recognition threshold
S URCES OF CONTAMINATION
Building maintenance materials including: paints, paint strippers, and other solvents; wood preserv-
atives, aerosol sprays, cleansers and disinfectants, moth repellents and air fresheners, stored
fuels
and automotive products, hobby supplies, dry cleaned clothing, etc..
EXPOSURE LIMITS
OSHA PEL: TWA: 300 ppm (1450 mg/cu m) STEL: 375 ppm (1800 mg/cu m)
NIOSH REL: TWA: 75 ppm (350 mg/cu m) STEL: 385 ppm (1800 mg/cu m)
ACGIH TLV: TWA: 300 ppm (1400 mg/cu m) STEL: 375 ppm (i750 mg/cu m)
EPA Ambient Air Standard: None established
TOXICITY
None determined
I
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HEALTH HAZARDS
May act as a simple asphyxiant. A narcotic in high concentration. Human dermal exposure to un-
diluted octane for five hours resulted in blister formation but no anesthesia; one hour caused
diffuse
burning sensation.
MEANS OF REDUCING EXPOSURE
1. Use household products according to manufacturer's directions.
2. Use outdoors or in well-ventilated places.
3. Throw away unused or little-used containers safely; buy in quantities that you will use soon.
MONITORING AND MEASUREMENT METHODS
NIOSH analytical method #1500, third edition
OSHA analytical method #07, second edition
L
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OZONE
MF:03 MW: 48.00
IDENTIFiCATION
Cas #: 10028-15-6 NIOSH: RS 8225000
SYNONYMS
Triatomic oxygen
APPEARANCE/ODOR
Colorless gas or dark blue liquid. Unstable. Pleasant, characteristic odor in concentrations ppm
CHEMICAUPHYSICAL PROPERTIES
Boiling Point: -111.9 C
Me9ting Point: -193 C
Vapor Pressure:
Specific Gravity (gas): 2.144 g/L
Odor threshold: none - pungent/thunderstorm
SOURCES OF CONTAMINATION
Electrical equipment, electrical air cleaners, outdoor sources.
EXPOSURE LIMITS
OSHA PEL: TWA: 0.1 ppm(0.2 mg/cu m) STEL: 0.3 ppm (0.6 mg/cu m)
NIOSH REL: Ceiling: 0.05 ppm
ACGIH TLV: STEL: 0.1 ppm (0.2 mg/cu m) - ceiling
EPA Ambient Air Standard: 235 ug/cu m/i hr
WHO Guidelines: 100-120 ug/cu m/8 hr; 150-200 ug/cu m/1 hr
ASHRAE Standard: 100 ug/cu m/continuous
Canadian Standard: 240 ug/cu m/1 hr
TOXICITY
Inhalation-human TCLo: 100 ppm/1 min
Inhalation-man TCLo: 1860 ppb/75 min
Inhalation-human LCLo: 50 ppm/30 min
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HEALTH HAZARDS
L
A human poison by inhalation. An experimental neoplastigen, tumorigen and teratogen. Human sys-
temic effects by inhalation: visual field changes, lacrimation, headache, decreased pulse rate with
fall
in blood pressure, blood pressure decrease, dermatitis, cough, dyspnea, respiratory stimulation and
other pulmonary changes. Experimental reproductive effects. Human mutagenic data. A skin, eye,
upper respiratory system and mucous membrane irritant. Concentration of 0.015 ppm of ozone in air
produces a barely detectable odor. Concentrations of 1 ppm produce a disagreeable sulfur-like odor
and may cause headache and irritation of eyes and the upper respiratory tract. Ozone is a common air
contaminant.
MEANS OF REDUCING EXPOSURE
1. To investigate general ventilation rates;
2. To investigate the possibility of local ventilation above the machine.
3. To locate the machine at a location where the pollution and exposure can be minimized; or
possibly
to confine the machine to specially partitioned rooms or compartments to prevent it from polluting
the
larger, general-use habitable space;
4. To find out if the manufacturer has introduced any modifications for reducing pollutant emission
of
the product; ifi no, search for a manufacturer that does;
5.To properiy operate and maintain the machine.
MONITORING AND MEASUREMENT METHODS
NIOSH analytical method P&CAM S8, S153, S154, volume 1, second edition.
OSHA Chemical Information Manual: IMIS 1980
N
I N
~
, t11
. D
~
~
~
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n-PENTADECANE
MF: C15H32 MW: 212.47
IDENTIFICATION
Cas #: 629-62-9 NIOSH: RZ 1800000
SYNONYMS
APPEARANCE/ODOR
Colorless liquid.
HEMICAUPHYSICAL PROPERTIES .~
~.~
Boiling Point: 270.5 C .~
Melting Point: 10 C
Vapor Pressure:
Specific Gravity: 0.770 @ 20 C/4 C
Odor threshold: ~
SOUR(MS OF CONTAMINATION
Building maintenance materials including: paints, paint strippers, and other solvents; wood preserv-
atives, aerosol sprays, cleansers and disinfectants, moth repellents and air fresheners, stored
fuels
and automotive products, hobby supplies, dry cleaned clothing, etc..
EXPOSURE LIMITS
OSHA PEL: None established
'
NIOSH REL: None established
ACGIH TLV: None established
EPA Ambient Air Standard: None established
TOXICITY
Intravenous-mouse LD50: 3494 mg/kg ~
~
~
~
~
~
~
~
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HEALTH HAZARDS
Moderately toxic by intravenous route.
MEANS OF REDUCING EXPOSURE
1. Use household products according to manufacturer's directions.
2. Use outdoors or in well-ventilated places.
3. Throw away unused or little-used containers safely; buy in quantities that you will use soon.
MONITORING AND MEASUREMENT METHODS
Gas chromatography analysis in air masses. [Neuling P et al; Qualitative and Quantitative Analysis
of
the N-alkanes C9-C17 and Pristane in Clean Air Masses; Fresenius' Z, Anal Chem 302(5) 375 (1980)].
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PERCHLOROETHYLENE
MF: C2CL4 MW: 165.82
IDENTIFICATION
Cas #: 127-18-4 NIOSH: KX 3850000
SYN ONYMS
1,1,2,2-tetrachloroethytene, ankilostin, antisol 1, carbon bichloride, carbon dichioride, didakene,
dow-
per, ethylene tetrachloride, perchlor, perchlorethylene, perclene, percosolve, perk, perklone,
persec,
tetlen, tetracap, tetrachioroethene, tetrachloroethylene, tetraleno, tetralex, tetravec, tetroguer,
tetropil
APPEARANCE/ODOR
Colorless liquid; ethereal odor
CHEMICAUPHYSICAL PROPERTIES
Boiling Point: 121.20 C
Melting Point: -23.35 C
Vapor Pressure: 15.8 mm Hg @ 22 C
Specific Gravity: 1.6311 @ 15 C/4 C
Odor threshold:
SOURCES OF CONTAMINATION
Household products
EXPOSURE LIMITS
OSHA PEL: TWA: 25 ppm (170 mg/cu m)
NIOSH REL: minimize exposure - carcinogenic
ACGIH TLV: TWA: 50 ppm (339 mg/cu m) STEL: 200 ppm (1370 mg/cu m)
EPA Ambient Air Standard:
WHO Guidelines: 5 mg/cu m/24 hr, 8 mg/cu m/30 min
TOXICITY
Inhalation-human TCLo: 96 ppm/7 hr
Inha.lation-man TCLo: 280 ppm/2 hr
Inhalation-man LDLo: 2857 mg/kg
Inhalation-man TCLo: 600 ppm/10 min
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HEALTH HAZARDS
Experimental poison by intravenous route. Moderately toxic to humans by inhalation with the follow-
ing effect: local anesthetic, conjunctiva irritation, general anesthesia, hallucinations, distorted
percep-
tions, coma and pulmonary changes. Moderately experimentally toxic by ingestion, inhalation,
intraperitoneal and subcutaneous routes. An experimental carcinogen and teratogen. Experimental
reproductive effects. Human mutagenic data. An eye and severe skin irritant.
MEANS OF REDUCING EXPOSURE
1. Follow label instructions carefully.
2. Throw away partially full containers of old or unneeded chemicals safely.
3. Buy limited quantities.
4. Keep exposure to perchloroethylene emissions from newly dry cleaned materials to a minimum.
MONITORING AND MEASUREMENT METHODS
NIOSH analytical method #1003, third edition
OSHA analytical method #07, second edition
L
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PETROLEUM SOLVENTS
MF: MW:
IDENTIFICATION
Cas #: NIOSH:
SYNONYMS
APPEARANCE/ODQR_
See individual solvents
CHEMICAUPHYSICAL PROPERTIES
Boiling Point:
Melting Point:
Vapor Pressure:
Specific Gravity:
Odor threshold:
SOURCES OF CONTAMINATION
Commercial cleaning products
EXPOSURE LIMITS
OSHA PEL: TWA: 400 ppm
NIOSH REL: TWA: 350 mg/cu m (except Kerosene) STEL: ceiling - 1800 mg/cu m
ACGIH TLV: See individual solvents
EPA Ambient Air Standard: none established
T XI .ITY
Refer to individual solvents
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HEALTH HAZARDS
May cause eye, nose and throat irritation. Skin irritant, mutagenic action when tested in cell
cultures,
nervous system effects.
MEANS OF REDUCING EXPOSURE
1. Use according to manufacturer's directions.
2. Use outdoors or in well-ventilated places.
3. Throw away unused or little-used containers safely; buy in quantities that you will use soon.
MONITORING AND MEASUREMENT METHODS
Refer to individual solvents
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PINE OIL
MR MW:
IDENTIFICATION
Cas #: 8002-09-3 NIOSH: TK 5100000
SYNONYMS
Oil of pine, oleum abietis, unipine, yarmor, yarmor pine oil
APPEARANCE/ODOR
Colorless to pale yellow liquid; turpentine-like odor.
CHEMICAUPHYSICAL PROPERTIES
Boiling Point: 200-220 C
Melting Point:
Vapor Pressure:
Specific Gravity: 0.86
Odor threshold:
SOURCES OF CONTAMINATION
Commercial cleaning products
EXPOSURE LIMITS
OSHA PEL: None established
NIOSH REL: None established
ACGIH TLV: None established
EPA Ambient Air Standard: None established
TOXICITY
Oral-man TDLo: 4700 mg/kg: central nervous system
Skin-rabbit LD50: 5 g/kg
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HEALTH HAZARDS
Moderately toxic by ingestion. Mildly toxic by skin contact. A weak allergen and a severe irritant
to
skin and mucous membranes. Human systemic effects by ingestion: excitement, ataxia, headache.
MEANS OF REDUCING EXPOSURE
1. Use according to manufacturer's directions.
2. Use outdoors or in well-ventilated places.
3. Throw away unused or little-used containers safely; buy in quantities that you will use soon.
MONITORING AND MEASUREMENT METHODS
No validated method found.
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POLYCHLORINATED BIPHENYLS (PCBs)
tvlF: iAw:
IDENTIFICATION
Cas #: 1336-36-3 NIOSH: TQ 1350000
YNONYM
Aroclor, chlophen, chiorextol, chlorinated biphenyl, chlorinated diphenylene, chloro biphenyl,
chloro-
1,1-biphenyl, clophen, dykanol, fenclor, inerteen, kanechlor, montar, noflamol, PCB, phenochlor,
pyralene, pyranol, santotherm sovol, therminol FR-1
APPEARANCE/ODOR
A series of technical mixtures consisting of many isomers and compounds that vary from mobile oily
li-
quids to white crystalline solids and hard noncrystalline resins.
CHEMICAUPHYSICAL PROPERTIES
Boiling Point: 340-375 C
Melting Point:
Vapor Pressure:
Specific Gravity: 1.44 @ 30 C
Odor threshold:
SOURCES OF CONTAMINATION
Electrical transformer, light-fixture transformer
EXPOSURE LIMITS
OSHA PEL: None established
NIOSH REL: Control to lowest feasible level
ACGIH TLV: None established
EPA Ambient Air Standard: None established
TOXICITY
Oral-rat TDLo: 16800 mg/kg/2 year
Oral-mouse LD50: 1900 mg/kg
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HEALTH HAZARDS
Moderately toxic by ingestion. Some are poisons by other routes. Suspected human carcinogens.
Experimental carcinogens and tumorigens. Experimental reproductive effects. The higher the
chlorine content of the diphenyl compound, the more toxic is it liable to be.
MEANS OF REDUCING EXPOSURE
1. Good operation and maintenance of the machines;
2. Decontaminate surface of these machines when necessary.
MONITORING AND MEASUREMENT METHODS
NIOSH analytical method #5503, third edition
L
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PROPYLBENZENE
MF: C9H12 MW: 120.21
IDENTIFICATION
Cas #: 103-65-1 NIOSH: DA 8750000
YN NYMS
Isocumene, 1-phenylpropane, n-propylbenzene
APPEARANCE/ODOR
Clear liquid.
CHEIy1ICAUPHYSICAL PROPERTIES
Boiling Point: 159.2 C
Melting Point: -99.5 C
Vapor Pressure: 10 mm Hg @ 43.3 C
Specific Gravity: 0.862
Odor threshold:
SOURCES OF CONTAMINATION
Building maintenance materials including: paints, paint strippers, and other solvents; wood preserv-
atives, aerosol sprays, cleansers and disinfectants, moth repellents and air fresheners, stored
fuels
and automotive products, hobby supplies, dry cleaned clothing, etc..
EXPOSURE LIMITS
OSHA PEL: None established
NIOSH REL: None established
ACGIH TLV: None established
EPA Ambient Air Standard: None established
TOXICITY ~
Inhalation-mouse LCLo: 20 g/cu m O
N
~
Oral-rat LD50: 6040 mg/kg ~
~11
~
~
~
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HEALTH HAZARDS
Mildly toxic by ingestion and inhalation.
MEANS OF REDUCING EXPOSURE
1. Use household products according to manufacturer's directions.
2. Use outdoors or in well-ventilated places.
3. Throw away unused or little-used containers safely; buy in quantities that you will use soon.
MONITORING AND MEASUREMENT METHODS
OSHA Chemical Information Manual: IMIS P107
I
N
p
~
. r©
~
~
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RADON
AF: Rn AW: 222
IDEMf IFICATION
Cas #: NIOSH:
SYNONYMS
APPEARANCE/ODOR
CoCorless, odorless, inert gas; very dense.
CHEMICAL/PHYSICAL PROPERTIES
Boiling Point: -62 C
Melting Point:
Vapor Pressure:
Specific Gravity: 9.73 g/L @ 1 atm (gas)
Odor threshold:
SOURCES OF CONTAMINATION
Concrete, brick, stone, soil, ground water, shower, earth and rock beneath home.
EXPOSURE LIMITS
OSHA PEL: None established
NIOSH REL: None established
ACGIH TLV: None established
EPA Ambient Air Standard: 4 PCi/L
WHO Guidelines: 2.6 PCi/L
ASHRAE Standard: 5.4 PCi/L
TOXICITY
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HEALTH HAZARDS
A common air contaminant. No immediate symptoms. Estimated to cause about 10% of lung cancer
deaths. Smokers are at higher risk of developing radon-induced lung cancer.
MEANS OF REDUCING EXPOSURE
1. Test your home for radon
2. Get professional advice before planning and carrying out radon reduction measures.
3. Seai cracks and other openings in basement floor.
4. Ventilate crawl space.
5. Install sub-slab ventilation or a heat recovery ventilator (air to air heat exchanger.)
6. Treat radon-contaminated well water by aerating or filtering through granulated-activated
charcoal.
MONITORING AND MEASUREMENT METHODS
"interim Indoor Radon Decay Product Measurement Protocois"'by USEPA, 1986. EPA publication
number: EPA 520/1-86-04.
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RESPIRABLE PARTICLES
MF: Mw:
IDENTIFICATION
Cas #: NIOSH:
SYNONYMS
APPEARANCE/ODOR
CHEMICAUPHYSICAL PROPERTIES
Boiling Point:
Melting Point:
Vapor Pressure:
Specific Gravity:
Odor threshold:
SOURCES OF CONTAMINATION !
~
Fireplaces, wood stoves, and kerosene heaters. Environmental tobacco smoke.
EXPOSURE LIMITS
OSHA PEL: None established
NIO SH REL: None established
ACGIH TLV: None established
EPA Ambient Air Standard: None established
TOXICI'TY .
N
0
~
~
HEALTH HAZARDS L/1
Eye, nose and throat irritation; respiratory infections and bronchitis; lung cancer (effects
attributable to ~
environmental tobacco smoke are listed under Tobacco Smoke)
~
0
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MEANS OF REDUCING EXPOSURE
1. Vent all furnaces to outdoors; keep doors to rest of house open when using unvented space
heaters.
2. Choose properly sized wood stoves, certified to meet EPA emission standards; make certain that
doors on all wood stoves fit tightly.
3. Have a trained professional inspect, clean, and tune-up central heating system (furnace, flues,
and
chimneys) annually. Repair any leaks promptly.
4. Change filters on central heating and cooling systems and air cleaners according to
manufacturer's
directions.
MONITORING AND MEASUREMENT METHODS
NIOSH analytical method #0600, third edition
L
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SODIUM CARBONATE
MF: C03*2Na MW: 105.99
IDENTIFICATION
Cas #: 497-19-8 NIOSH: VZ 4050000
SYNONYMS
Carbonic acid, disodium salt; crystal carbonate; disodium carbonate, soda ash, trona
APPEARANCE/ODOR
White, odoriess, small crystals or crystalline powder; alkaline taste.
CHEMICAUPHYSICAL PROPERTIES
Boiling Point: decomposes
Melting Point: 851 C
Vapor Pressure:
Specific Gravity: 2.509 @ 0 C
Odor threshold:
SOURCES OF CONTAMINATION
Commercial cleaning product, photography
EXPOSURE LIMITS
OSHA PEL:
NIOSH REL:
ACGIH TLV:
EPA Ambient Air Standard:
TOXICITY
Inhalation-rat LC50: 2300 mg/cu m/2 hr
Inhalation-mouse LC50: 1200 mg/cu m/2 hr
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HEALTH HAZARDS
Poison by intraperitoneal route. Moderately toxic by inhalation and subcutaneous routes. Mildly
toxic
by ingestion. Experimental reproductive effects. A skin and eye irritant.
MEANS OF REDUCING EXPOSURE
i. Use according to manufacturer's directions.
2. Use outdoors or in well-ventilated places.
3. Throw away unused or little-used containers safefy; buy in quantities that you will use soon.
MQNLTORING AND MEASUREMENT METHODS
Titrate with 0.5 N HCI., using methyl orange, & note total alkalinity found. [AOAC. 10th edition
1965
and following EDS 13/71 5.019]
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SODIUM PERBORATE
MF: B03*Na MW: 81.80
lDENTiFICATION
Cas #: NIOSH: ED 4800000
SYNONYMS
Boric acid, sodium salt; sodium peroxyborate, sodium peroxoborate
APPEARANCE/ODOR
Tetrahydrate, white, odorless, crystalline powder. Saline taste.
CHEMICAUPHYSICAL PROPERTIES
Boiling Point: Decomposes above 60 C
Melting Point:
Vapor Pressure:
Specific Gravity:
Odor threshold:
SOURCES OF CONTAMINATION
Commercial cleaning product
EXPOSURE LIMITS
OSHA PEL: None established
NIOSH REL: None established
ACGIH TLV: None established
EPA Ambient Air Standard: None established
TOXICfTY
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HEALTH HAZARDS
Mutagenic data. A powerful oxidizer.
MEANS OF REDUCING EXPOSURE
1. Use according to manufacturer's directions.
2. Use outdoors or in well-ventilated places.
3. Throw away unused or little-used containers safely; buy in quantities thatyou will use soon.
MONITORING AND MEASUREMENT METHODS
EPA Method 200.7: an inductively coupled plasma-atomic emission spectrophotmetric method for the
determination of dissolved, suspended, or total elements in drinking water, surface water, and
domes-
tic and industrial wastewater, is described. Sodium is analyzed at a wavelength of 588.995 nm and
has an estimated detection limit of 29 ug/1. /Total Sodium/ [40 CFR 136 (7/1/88)]
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SODIUM PHOSPHATE
MF:04P*3Na MW: 163.94
i DEN'i"I FICATION
Cas #: 7601-54-9 NIOSH: TC 9490000
SYNONYMS
Dri-tri, nutrifos STP; phosphoric acid, trisodium solt; trisodium phosphate; sodium phosphate, an-
hydrous; sodium phosphate, tribasic (DOT); tribasic sodium phosphate; tromete; TSP
APPEARANCEIODOR
Dodecahydrate, colorless or white crystals
CHEMICAUPHYSICAL PROPERTIES
Boiling Point:
Melting Point: 75 C
Vapor Pressure:
Specific Gravity: -1.6
Odorthreshold:
SOURCES OF CONTAMINATION
Commercial cleaning product,Ephotographic developers
EXP SURE LIMITS
OSHA PEL: None established
NIOSH REL: None established
ACGIH TLV: None established
EPA Ambient Air Standard: None established
T XIC(TY
IV
C
Oral-rats LD50: 7.4 glkg ~
~
~
~
~
~
~
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HEALTH HAZARDS
Moderately toxic by intravenous route. Mutagenic data. A strong, caustic material.
I
MEANS OF REDUCING EXPOSURE
1. Use according to manufacturer's directions.
2. Use outdoors or in well-ventilated places.
3. Throw away unused or little-used containers safe(y; buy in quantities that you will use soon.
MQNITORiNG AND MEASUREMENT METHODS
No validated method found
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SODIUM DODECYL SULFATE
MF: C12H2604S*Na MW: 289.43
IDENTIFICATION
Cas #: 151-21-3 NIOSH: WT 1050000
SYN NYM
Sulfuric acid, monododecyl ester, sodium salt; aquarex methyl; carsonol sis; cycloryi 21; detergent
66;
dodecyl sulfate, sodium salt; dreft duponol; irium; richonol C; sipex OP; dodecyl sodium sulfate;
ultra
sulfate SL-1, etc.
APPEARANCElODOR
White to cream-colored crystals, flakes or powder water, water-sol. ,
CHEMICAL/PHYSICAL PROPERTIES
Boiling Point:
Melting Point:
Vapor Pressure:
Specific Gravity:
Odor threshold:
SOURCES OF CONTAMINATION
Carpet shampoo.
EXPOSURE LIMITS
OSHA PEL: None established
NIOSH REL: None established
ACGIH TLV: Mone established
EPA Ambient Air Standard: None established
TOXICI"TY
Skin-human 250 mg/24 hr mild
Oral-rat LD50: 1288 mg/kg
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HEALTH HAZARDS
Poison by intravenous and intraperitoneal routes. Moderately toxic by ingestion. An experimental
teratogen. Experimental reproductive effects. A human skin irritant. An experimental eye and sever
skin irritant. A mild allergen. Mutagenic data.
MEANS OF REDUCING EXPOSURE
1. Use according to manufacturer's directions.
2. Use outdoors or in well-ventilated places.
3. Throw away unused or little-used containers safely; buy in quantities that you will use soon.
MONITORING AND MEASUREMENT METHODS
None found
I
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SULFUR DIOXIDE
MF:02S MW: 64.06
iDENTIFICATION
Cas #: 7446-09-5 NIOSH: WS 4550000
SYNO_NYM_S
Bisulfite, fermenicide liquid, fermenicide powder, sulfurous acid anhydride, sulfurous anhydride,
sul-
furous oxide, sulfur oxide
APPEARANCE/ODOR
Colorless gas or liquid, pungent odor.
CHEMICAL/PHYSICAL PROPERTIES
Boiling Point: -10.0 C
Melting Point: -72.7 C
Vapor Pressure: 49.6 mm Hg @ 21.1 C
Specific Gravity: 1.434 @ 0 C (liquid)
Odor threshold: 2.7 ppm - detection threshold (sharp irritating)
4.4 ppm - recognition threshold
SOURCES OF CONTAMINATION
Combustion sources including gas ranges, dryers, water heaters, kerosene heaters, fireplaces and
wood stoves, gas stove, garages, outdoor sources, chimneys, furnaces
EXPOSURE LIMITS
OSHA PEL: TWA: 2 ppm (5 mg/cu m) STEL: 5 ppm (10 mg/cu m)
NIOSH REL: TWA: 0.5 ppm (1.3 mg/cu m)
ACGIH TLV: TWA: 5 ppm (5.2 mg/cu m) STEL: 5 ppm (13 mg/cu m)
EPA Ambient Air Standard: None established
TOXI ITY
Inhalation-man TCLo: 4 ppm/1 min
Inhalation-human TCLo: 3 ppm/5 days
Inhalation-human LCLo: 1000 ppm/10 mins
Inhalation-human LCLo: 3000 ppm/5 mins
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HEALTH HAZARDS
i
A poison gas. Moderately toxic experimentally by inhalation. Mildly toxic to humans by inhalation.
An
experimental tumorigen and teratogen. Human systemic effects by inhalation: pulmonary vascular
resistance, respiratory depression and other pulmonary changes. It chiefly affects the upper
respiratory tract and the bronchi. it may cause edema of the lungs or glottis and can produce
respiratory paralysis. Experimental reproductive effects. Human mutagenic data. A corrosive irritant
to eyes, skin and mucous membranes. 400-500 ppm is immediately dangerous to life and 50-100 ppm
is considered to be the maximum permissible concentration for exposure of 30-60 minutes. It is a
common air contaminant.
MEANS OF REDUCING EXPOSURE
1. Keep gas appliance properly adjusted.
2. Consider purchasing vented gas space heaters and furnaces.
3. Use proper fuel in kerosene space heaters.
4. Install and use exhaust fan vented to outdoors over gas stoves.
5. Open flues when gas fire-places are in use.
6. Choose properly sized wood stoves that are certified to meet EPA emission standards. Make cer-
tain that doors on all wood stoves fit tightly.
7. Have a trained professional inspect, clean and tune-up central heating system (furnaces, flues,
and
chimneys) annually. Repair any leaks properly.
8. Do not idle car inside garage.
MONITORING AND MEASUREMENT METHODS
NIOSH analytical method #6004, third edition
OSHA analytical method #107, #104, second edition
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TETRADECANE
MF: C14H30 MW: 198.44
IDENTIFICATlON
Cas #: 629-59-4 NIOSH: XB 8000000
SYNONYMS
APPEARANCE/ODOR
Colorless liquid.
CHEMfCAUPHY ICAL PROPERTIES
Boiling Point: 252-255 C
Melting Point: 5.5 C
Vapor Pressure: 1 mm Hg @ 76.4 C
Specific Gravity: 0.765 @ 20 C/4 C
Odor threshold:
SOUR ;ES OF CONTAMINATION
Building maintenance materials including: paints, paint strippers, and other solvents; wood preserv-
atives, aerosol sprays, cleansers and disinfectants, moth repellents and air fresheners, stored
fuels
and automotive products, hobby supplies, dry cleaned clothing, etc..
EXPOSURE LIMITS
OSHA PEL: None established
NIOSH REL: None established
ACGIH TLV: None established
EPA Ambient Air Standard: None established
TOXICITY
Skin-mouse TDLo: 9600 mg/kg/20 week
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HEALTH HAZARDS
An experimental tumorigen. Probably irritating and narcotic in high concentrations.
MEANS OF REDUCING EXPOSURE
1. Use household products according to manufacturer's directions.
2. Use outdoors or in well-ventilated places.
3. Throw away unused or little-used containers safely; buy in quantities that you will use soon.
MONITORING AND MEASUREMENT METHODS
No validated method found.
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TOLUENE
MF: C7H8 MW: 92.15
IDENTIFICATION
Cas #: 108-88-3 NIOSH: XS 5250000
SYNONYMS
Antisal la, methacide, methylbenzene, methylbenzol, NCI-C07272, phenylmethane, RCRA waste num-
ber U220, toluol, toluol, tolu-sol
APPEARANCE/ODOR
Colorless liquid; benzol-like odor.
CHEMfCAL/PHYSICAL PROPERTIES
Boiling Point: 110.4 C
Melting Point: -95 C to -94.5 C
Vapor Pressure: 36.7 C mm Hg @ 30 C
Specific Gravity: 0.886 @ 20 C/4 C
Odor threshold: 1.6 ppm - detection threshold (sour/burnt)
11 ppm - recognition threshold
SOUR ,ES OF_ CONTAMINATION
Building maintenance materials including: paints, paint strippers, and other solvents; wood preserv-
atives, aerosol sprays, cleanser's-and disinfectants, moth repellents and air fresheners, stored
fuels
and automotive products, hobby supplies, dry cleaned clothing, etc..
EXPO URE LIMITS
OSHA PEL: TWA: 100 ppm (375 mg/cu m) STEL: 150 ppm (560 mg/cu m)
NIOSH REL: IWA: 100 ppm (375 mg/cu m) STEL: 200 ppm (750 mg/cu m)
ACGIH TLV: TWA: 100 ppm (377 mg/cu m) STEL: 150 ppm (565 mg/cu m)
EPA Ambient Air Standards: None established
N
G~
TOXICITY
N
C1t
lnhalation-human TCLo: 200 ppm ~
Inhalation-man TCLo: 100 ppm: central nervous system ~
kA
Q
44
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HEALTH HAZARDS
Poison by intraperitoneal route. Moderately toxic by intravenous, subcutaneous and possibly other
route. Mildly toxic by inhalation. An experimental teratogen. Human systemic effects by inhalation:
central nervous system changes, 'hallucinations or distorted perceptions, motor activity changes,
antip-
sychotic, psychophysiological test changes and bone marrow changes. Experimental reproductive ef-
fects. Mutagenic data. A human eye irritant. An experimental skin and severe eye irritant.
MEANS OF REDUCING EXPOSURE
1. Use household products according to manufacturer's directions.
2. Use outdoors or in well-ventilated places.
3. Throw away unused or little-used containers safely; buy in quantities that you will use soon.
MONITORING AND MEASUREMENT METHODS
NIOSH analytical method #1500, #1501, #4000, third edition
OSHA Chemical Information Manual: IMIS 2460
I
I - N
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1,1,1-TRICHLOROETHANE
MF: C2H3C13 MW: 133.40
IDENTIIFICATION
Cas #: 71-55-6 NIOSH: KJ 2975000
SYNONYMS
aerothene TT, chloroetene, chloroethene, chiorothane NU, chlorothene, methylchloroform,
methyltrichloromethane, strobane, 1,1,1, TCE, alpha-trichioroethane, tri-ethane, NIC-C04626, RCRA
waste number U226
APPEARANCE/ODOR
Colorless liquid.
CHEMICAL/PHYSICAL PROPERTIES
Boiling Point: 74.1 C
Melting Point:
Vapor Pressure: 100 mm Hg @ 20 C
Specific Gravity: 1.3376 @ 20 C/4 C
Odor threshold: 390 ppm - detection threshold (sweet/etherish)
710 ppm - recognition threshold
SOURCES OF CONTAMINATION
Building maintenance materials including: paints, paint strippers, and other solvents; wood preserv-
atives, aerosol sprays, cleansers and disinfectants, moth repellents and air fresheners, stored
fuels
and automotive products, hobby supplies, dry cleaned clothing, etc..
EXP URE LIMITS
OSHA PEL: TWA: 350 ppm (1900 mg/cu m) STEL: 450 ppm (2450 mg/cu m)
NIOSH REL: STEL: 350 ppm (1910 mg/cu m)
ACGIH TLV: TWA: 350 ppm (1910 mg/cu m) STEL: 450 ppm (2460 mg/cu m)
EPA Ambient Air Standards: None established
TOXICIlY
Inhalation-human TCLo: 920 ppm/70 min
Inhalation-man TCLo: 350 ppm: central nervous system
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HEALTH HAZARDS
Poison by intravenous route. Moderately toxic by ingestion, inhalation, skin contact, subcutaneous
and intraperitoneal routes. An experimental teratogen. Human systemic effects by ingestion and in-
halation: conjunctiva irritation, hallucinations or distorted perceptions, motor activity changes,
ir-
ritability, aggression, hypermotility, diarrhea, nausea or vomiting and other gastrointestinal
changes.
Experimental reproductive effects. Mutagenic data. A human skin irritant. An experimental skin and
severe eye irritant. Narcotic in high concentrations.
MEANS OF REDUCING EXPOSURE
1. Use household products according to manufacturer's directions.
2. Use outdoors or in well-ventilated places.
3. Throw away unused or little-used containers safely; buy in quantities that you will use soon.
MONITORING AND MEASUREMENT METHODS
NIOSH analytical method #1003, third edition
OSHA method #14, second edition
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n-TRIDECANE
MF: C13H28 MW: 184.41
1 DENTI FICATION
Cas #: 629-50-5 NIOSH: YD 3025000
S_YNONYMS
Tridecane
APPEARANCE/ODOR
Colorless liquid
CHEMICAL/PHYSICAL PROPERTIES
Boiling Point: 234 C
Melting Point: -6.2 C
Vapor Pressure:
Specific Gravity: 0.757 @ 20 C/4 C
Odor threshold:
SOURC;ES OF CONTAMINATION
Building maintenance materials including: paints, paint strippers, and other solvents; wood preserv-
atives, aerosol sprays, cleansers and disinfectants, moth repellents and air fresheners, stored
fuels
and automotive products, hobby supplies, dry cleaned clothing, etc..
EXPOSURE LIMITS
OSHA PEL: None established
NIOSH REL: None established
ACGVH TLV: None established
EPA Ambient Air Standards: None established
TOXICITY
Intravenous-mouse LD50: 1161 mg/cu m
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HEALTH HAZARDS
Moderately toxic by intravenous route.
MEANS OF REDUCING EXPOSURE
1. Use household products according to manufacturer's directions.
2. Use outdoors or in well-ventilated places.
3. Throw away unused or little-used containers safely; buy in quantities that you will use soon.
MONITORING AND MEASUREMENT METHODS
The alkanes to C17 may be collected on charcoal, the higher members as particulate matter on
filters,
and determined by gas chromatography. Meites L, 1963. /Alkanes/ [Patty. Industrial Hygiene and
Toxicology, 3rd edition, Volume 2A, 213, 2C, 1981-82, p. 31941
n solation by steam distillation and analysis of sediment by gas chromatography-flame ionization.
[I3elisle AA, Gay ML; Isolationof hydrocarbon residues from sediment by steam distillation; Bull En-
vironmental Contamination Toxicology 29(5) 539 (1982)].
No validated method found.
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VINYL CHLORIDE
MF: C2H3C1 MW: 62.50
l D ENTI FICATION
Cas #: 75-01-4 NIOSH: KU 9625000
YN NYMS
Chiorethene, chlorethylene, chloroethene, chloroethylene, ethylene monochloride, monochloroethene,
trovidur, VC, VCM, vinyl chloride monomer, vinyl C monomer
APPEARANCE/ODOR
Colorless liquid or gas; faintly sweet odor.
CHEMNCALIPHYSICAL PROPERTIES
Boiling Point: -13.9 C
Melting Point: -160 C
Vapor Pressure: 2600 mm Hg @ 25 C
Specific Gravity: 0.9195 @ 15 C/4 C (liquid)
Odor threshold: none - sweet
SOUR ES OF CONTAMINATION
Aerosol spray, propellants, and solvents
EXP URE L1MfTS
OSHA PEL: TWA: 1 ppm STEL: 5 mg/cu m - ceiling
NIOSH REL: TWA: lowest feasible Ceiling: 0.5 ppm (carcinogen)
ACGIH TLV: TWA: 5 ppm (13 mg/cu m) - confirmed human carcinogen
EPA Ambient Air Standard:
TOXIC1iY
Inhalation-man TCLo: 30 mg/cu m (5 year male)
Inhalation-human TC: 300 mg/cu m
Inhalation-man TCLo: 500 ppm/7 hr
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HEALTH HAZARDS
Poison by inhalation. Moderately toxic by ingestion. A human carcinogen which causes liver and
blood tumors. An experimental carcinogen, tumorigen and teratogen. Human reproductive effects by
inhalation: changes in speratogenesis. Human mutagenic data. A severe irritant to skin, eyes, and
mucous membranes. In high concentration it acts as an anesthetic. Chronic exposure has shown
liver injury.
MEANS OF REDUCING EXPOSURE
1. To increase ventilation rate when operating such devices;
2. To use a product that does not pollute indoor air environment to substitute vinyl chloride.
MONITORING AND MEASUREMENT METHODS
NIOSH analytical method #1007, #178, third edition.
OSHA analytical method #04, #75, second edition
I
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m-XYLENE
MF: C8H10 MW: 106.18
IDENTIFICATION
Cas #: 108-38-3 NIOSH: ZE 2275000
SYNONYMS
APPEARANCE/ODOR
Colorless mobile, flammable, liquid
CHEMICAL/PHYSICAL PROPERTIES
Boiling Point: 139 C
Melting Point: -47.9 C
Vapor Pressure: 10 mm Hg @ 28.3
Specific Gravity: 0.864 @ 20 CJ4 C
Odor threshold: 0.62 ppm - detection threshold
SOURC;ES OF CONTAMINATION
Building maintenance materials including: paints, paint strippers, and other solvents; wood preserv-
atives, aerosol sprays, cleansers and disinfectants, moth repellents and air fresheners, stored
fuels
and automotive products, hobby supplies, dry cleaned clothing, etc..
EXPOSURE LIMITS
OSHA PEL: TWA: 100 ppm (435 mg/cu m) STEL: 150 ppm (655 mg/cu m)
NIOSH REL: TWA: 100 ppm (434 mg/cu m) STEL: 200 ppm (868 mg/cu m)
ACGIH TLV: TWA: 100 ppm (434 mg/cu m) STEL: 150 ppm (651 mg/cu m)
TOXICLIY
Inhalation-man TCLo:424 mg/m3/6 hr/6 day:central nervous system
Inhalation-man TCLo: 870 mg/cu m/4 hr-l:central nervous system
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HEALTH HAZARDS
Mildly toxic by ingestion. A severe skin and eye irritant.
MEANS OF__REDUClNG_EXPOSURE
1. Use household products according to manufacturer's directions.
2. Use outdoors or in well-ventilated places.
3. Throw away unused or little-used containers safely; buy in quantities that you will use soon.
MONITORING AND MEASUREMENT METHODS
NIOSH analytical method #1501, third edition
OSHA analytical method #07, second edition
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o-XYLEN E
MF: C8H10 MW: 106.18
IDENTIFICATION
Cas #: 95-47-6 NIOSH: ZE 2450000
SYNONYMS
o-dirnethylbenzene, 1,2-dimethylbenzene, o-methyltoluene, 1,2-xyiene, o-xylol (DOT)
APPEARANCE/ODOR
Colorless liquid
CHEMICAL/PHYSICAL PROPERTIES
Boiling Point: 144.4 C
Melting Point: -25.2 C
Vapor Pressure:
Specific Gravity: 0.880 @ 20 C/4 C
Odor threshold: 5.4 ppm - detection threshold
SOURCES OF CONTAMINATION
Building maintenance materials including: paints, paint strippers, and other solvents; wood preserv-
atives, aerosol sprays, cleansers and disinfectants, moth repellents and air fresheners, stored
fuels
and automotive products, hobby supplies, dry cleaned clothing, etc..
EXPOSURE LIMITS
OSHA PEL: TWA: 100 ppm (435, mg/cu m) STEL: 150 ppm (655 mg/cu m)
NIOSH REL: TWA: 100 ppm (434 mg/cu m) STEL: 200 ppm (868 mg/cu m)
ACGIH TLV: TWA: 100 ppm (434 mg/cu m) STEL: 150 ppm (651 mg/cu m)
TOXICITY
lnhalation-rat LCLo: 6125 ppm/12 Hr
Inhalation-mouse LCLo: 30 g/cu m
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HEALTH HAZARDS
Moderately toxic by intraperitoneal route. Mildly toxic by ingestion and inhalation. An experimental
teratogen. A common air contaminant.
MEANS OF REDUCING EXPOSURE
1. Use household products according to manufacturer's directions.
2. Use outdoors or in well-ventilated places.
3. Throw away unused or little-used containers safely; buy in quantities that you will use soon.
MONlTORING AND MEASUREMENT METHODS
NIOSH analytical method #1501
OSHA analytical method #07, second edition
L
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p-XYLEN E
MF: C8H10 MW: 106.18
IDENTIFICATION
Cas #: 106-42-3 NIOSH: ZE 2625000
SYNONYM
Chromar, p-dimethylbenzene, 1,4-dimethylbenzene, p-methyltoluene, scintillar, 1,4-xylene, p-xylol
APPEARANCE/ODOR
Colorless plates or prisms
CHEMhCAL/PHYSICAL PROPERTIES
Boiling Point: 138.3 C
Melting Point: 13-14 C
Vapor Pressure: 10 mm Hg @ 27.3
Specific Gravity: 0.8611 @ 20 C/4 C
Odor threshold: 2.1 ppm - detection threshold
SOURCES OF CONTAMINATI N
Bui(cfing maintenance materials including: paints, paint strippers, and other solvents; wood
preserv-
atives, aerosol sprays, cleansers and isinfectants, moth repellents and air fresheners, stored fuels
and
automotive products, hobby supplies, dry cleaned clothing, etc..
EXPOSURE LIMITS
OSHA PEL: TWA: 100 ppm (435 mg/cu m) STEL: 150 ppm (655 mg/cu m)
NIOSH REL: TWA: 100 ppm (434 mg/cu m) STEL: 200 ppm (868 mg/cu m)
ACGIH TLV: TWA: 100 ppm (434 mg/cu m) STEL 150 ppm (651 mg/cu m)
TOXICITY
Inhalation-rat LC50: 4550 ppm/4 hr
Inhalation-mouse LCLo: 15 g/cu m
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HEALTH HAZARDS
Moderately toxic by intraperitoneal route. Mildly toxic by ingestion and inhalation. An experimental
teratogen. Experimental reproductive effects. May be narcotic in high concentrations. Chronic
'toxicity not established, but is less toxic than benzene.
MEANS OF REDUCING EXPOSURE
1. Use household products according to manufacturer's directions.
2. Use outdoors or in well-ventilated places.
3. Throw away unused or little-used containers safely; buy in quantities that you will use soon.
MONITORING AND MEASUREMENT METHODS
NIOSH analytical method #1501
OSHA analytical method #07, second edition
I N
O
tJ
N
~
~
O
N+
W
%3
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Chapter VI Protocols For Indoor Air Quality Investigations
1. Methodology
A consistent, solution-oriented approach should be adopted by the investigator(s) when conducting
an indoor air quality investigation. This approach should systematically exclude a continually
narrow-
ing range of possibilities. Generally, this exclusion hierarchy involves evaluation of physical,
chemical
and microbiological factors, in the order presented.
Based on the information obtained during initial conversation with the requestor, the following
respon
ses by the investigator(s) are possible:
a. To provide "self-heip evaluation" materials to the requestor. Remain available for consultation
by
telephone. Become more involved, if necessary.
b. To conduct an initial evaluation and provide recommendations to solve the problem or for further
study on a "self-help" basis.
c. To conduct a full scale investigation.
The team of investigators for a full scale investigation should include an industrial hygienist and
a
physician/epidemiologist, but can also include other professionals such as an engineer. Most inves-
tigations contain the following parts: background assessment, initial site assessment, and, if
neces-
sary, additional site assessment:
2. Background Assessment
For the background assessment, the investigator(s) should obtain, by telephone, as much information
on the building/house as practical; an idea of symptoms being experienced, and a chronology of the
problem. Much of this information can also be collected using a standard questionnaire. Copies of
other previous investigations which are,relevant to the problem should be requested. These data are
then used to tailor the protocol for the initial site assessment so as to make it more efficient.
3. Initial Site Assessment
The initial site assessment includes five separate steps or parts: an opening conference, a walk-
through evaluation, personal interviews, phase I of environmental monitoring, and a closing con-
ference.
a. Opening Conference - The opening conference is attended by occupiers and their employees or
residents of the building, as well as someone who has knowledge of the operation, and maintenance
of the building's heating, ventilating and air conditioning (HVAC) systems. This meeting serves to
present the role of the investigator(s), discusses anticipated activities and arranges to receive
copies
of pertinent data not yet received.
b. Walk-through Survey - The walk-through survey should involve all or part of the building
including
inspection of the HVAC systems with special attention given to the mechanism by which outside air
enters each HVAC unit. Architectural plans and ventilation test and balance reports may also be
reviewed during this phase. Potential sources of emission are identified so that each may be further
evaluated, as needed.
c. Personal Interview - Personal Interviews are often conducted to determine the extent, prevalence
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and character of reported symptoms. The use of a questionnaire, such as the one shown in Appendix
11, may be the most efficient means of collecting this type of information. It can be used as a
guide
during personal interviews or it can be self-administered.
d. Phase I Environmental Monitoring - Phase I environmental monitoring is usually conducted on each
initial survey. The scope of this effort may vary, but usually will either evaluate certain aspects
of the
building environment, which are important factors in all investigations, or explore any other pos-
sibilities made apparent from the background assessment. Evaluation of the ventilation system using
both actual measurement and/or carbon dioxide (C02) techniques, and monitoring temperature and
relative humidity are useful procedures for all evaluations during the initial site assessment.
Monitoring
for formaldehyde is an example of a specific method which may be used if the background assess-
ment indicates that respiratory system and eye irritation are prevalent complaints and the space has
been recently built or renovated (a number of furnishings are potential sources of formaldehyde).
Most of the monitoring accomplished on the initial survey is obtained using direct-reading
instruments
where possible because they provide results on-the-spot. Any deficiencies noted can be corrected
and re-evaluated. Trace concentrations of hundreds of compounds could be identified depending on
the extent of the sampling and analytical effort; however, the concentrations usually detected would
not be expected to cause adverse health effects in a normal healthy individual.
e. Evaluating HVAC Systems - HVAC systems can be complicated and most industrial hygienists have
received very little or no training in the design, maintenance and trouble-shooting of building
ventila-
tion systems. The most important aspect of evaluating HVAC systems is to gain an understanding of
how they are supposed to be working and then use some relatively simple methods to assure that the
system is performing up to the design specifications. To decide whether this is adequate with
respect
to the complaint areas in the building/house, return to the complaint area(s) and measure supply and
return air flows using either a velometer or a flow hood and compare the results to the design quan-
tities. Note that in variable-air-volume (VAV) systems the supply air flows may vary during the day.
f. Monitoring Temperature and Relative Humidity - Temperature too cold, too warm or fluctuating can
be a source of complaints. While individuals vary in their limits of thermal comfortability, if a
significant
number of workers complain (more than 20%), then temperature and relative humidity may be creat-
ing an uncomfortable environment. If temperatures are too warm, complaints or tiredness, lack of
con-
centration and headache may also be reported. Low relative humidities, not uncommon in the winter
in a building or residence that is not humidified, can cause eye, nose and throat irritation.
4. Closing Conference
The closing conference of the initial site survey provides an opportunity for the investigator(s) to
present the activities accomplished, any results obtained and recommendations on corrective actions
if potential problems were identified. If no problems were identified, recommendations may be made
on how to continue studying the problem either on a self-help basis or through continued involvement
by the investigator(s). Typical recommendations, when a probable explanation for the reported
symptoms are not identified, would Include the formulation of a more formalized method of reporting
worker symptoms on a daily basis and the generation of HVAC data logs to provide evidence that the
HVAC system is performing in a consistent manner overtime.
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Guide to Indoor Air Pollutants
5. Additional Site Assessments
If the background assessment and the initial site visit identify a problem that need further
definition, or
if no problem can be isolated, an additional site assessment may be performed. During the additional
site assessment, more specific and extensive monitoring may be conducted for chemical and/or
microbiological contaminants of interest. Sampling for airborne microbiological contaminants is also
outside of what is considered a standard industrial hygiene technique. Useful techniques are still
under evaluation. Methodology is available; however, analytical support is somewhat limited. Never-
theless, the topic of potential microbiological contamination usually comes up as an investigation
progresses. Close visual inspection of the various HVAC components will usually uncover a
microbiological problem If present.
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Guide to Indoor Air Pollutants
Chapter VII Indoor Air Quality Program of Detail Associates, Inc.
Detail Associates, Inc. started its Indoor Air Quality Investigation Program back in late 1970's
when the
problem of indoor air quality in modern buildings was not yet given as much attention by the public
as
today. The problem was then called "hypersensitivity pneumonitis" in North America and is today
given a
more understandable name - "Sick Building Syndrome".
After successfully providing assessment and engineering control services in this field and
constantly em-
phasizing research and development for the last ten years, the Program is now capable of undertaking
projects ranging from overview indoor air quality assessments to complex industrial hygiene
investigations
incorporating environmental-medical research.
The program studies the indoor air quality of a client through a number of sophisticated testing
methods in-
cluding:
Chemical Parameter Testing - often includes real-time analysis of airborne contaminant gases
such as carbon monoxide; carbon dioxide; hydrogen sulfide; formaldehyde; petroleum hydrocar-
bons; ozone and organic vapors.
Physical Testing - allows on-site measurements of temperature, humidity and airflow relationships
with which the diagnosis of HVAC inefficiencies and limitations can be accurately achieved and
reviewed against chemical testing and blo-aerosol analytical data.
Bio-aerosol testing - utilizes bio-test airborne sampling technology and swab-surface collection
techniques for qualitative and quantitative analysis of micro-organisms associated with the sam-
pling local.
The IAQ specialists of the program compare the results of testing with current public health
standards
and/or recommendations of the relevant governmental agencies and private research institutions to
assess
for any presence and the extent of indoor air quality problem(s).
For more information about the program, contact Detail Associates, Inc.; 300 Grand Avenue,
Englewood,
NJ 07631. Telephone: (201) 569-6708. Fax: (201) 569-4378.
Detail Associates, Inc. 203

Guide to Indoor Air Pollutants
204 Detail Associates, inc..

Guide to Indoor Air Pollutants
Chapter VIII Recommended Sources of Information
Federal Agencies
Federal agencies with indoor air responsibilities are listed below. Write or phone them for free
information
materials theyy have.
U.S. Environmental Protection Agency
Public Information Center
401 M Street SW, Washington, DC 20460.
Tel: 202-382-2080
Operates Monday to Friday from 8:00 to 17:30 (EST)
Other EPA Public Inquiry Phone Numbers
National Telecommunications Network
1-800-858-PEST (out of Texas)
1-806-743-3091 (in Texas)
Provides information about pesticides to the general public and the medical, veterinary, and profes-
sional communities.
TSCA Assistance Information Service
202-554-1404
Operates Monday to Friday 8:30 to 17:00 (EST)
Provides information on regulations under the Toxic Substances Control Act (TSCA) and on EPA's as-
bestos program.
Safety Drinking Water Hotline
202-382-5533
Operates Monday to Friday from 8:30 to 16:30 (EST)
Provides information on regulations under the Safe Drinking Water Act, radon in drinking water, and
a
list of state drinking water offices.
RCRA/Superfund Hotline
1-800-424-9346 (Nationwide)
1-202-382-3000 (In Washington)
Operates Monday to Friday from 8:30 to 19:30 (EST)
Provides information on regulations under both the Resource Conservation and Recovery Act and the
Superfund Law.
U.S. Consumer Product Safety Commission (CPSC)
Washinciton, DC 20207
Tel: 1-800-638-CPSC (Product Safety)
Operates Monday to Friday from 10:30 to 16:00 (EST)
Recorded information is available 24 hours daily
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Guide to Indoor,Air Pollutants
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Other Federal Agencies
Bonneville Power Administration
Portland, OR 97208
General Services Administration
18th and F Streets NW, Washington, DC 20450
Office of Conservation and Renewable Energy
U.S. Department of Energy
1000 Independence Avenue SW, Washington, DC 20585.
National Institute for Occupational Safety and Health
Hazard Evaluations and Technical Assistance Branch (R-9)
Division of Surveillance, Hazard Evaluations and Field Studies
U.S. Department of Health and Human Services
4676 Columbia Parkway, Cincinnati, Ohio 45226.
Office on Smoking and Health
U.S. Department of Health and Human Services
Rockville, MD 20857.
Office on Energy and the Environment
U.S. Department of Housing and Urban Development
Washington, DC 20410.
Occupational Safety and Health Administration
U.S. Department of Labor
200 Constitution Avenue NW, Washington, DC 20210
Tennessee Valley Authority
Industrial Hygiene Branch
328 Multipurpose Building, Muscle Shoals, AL 35660
State and Local Agencies
The EPA publication, "Directory of State Indoor Air Contacts", lists state agency contacts and is
avail-
able from the Public Information Center of EPA.
Private Sector Contacts
American Institute of Architects
1350 New York Avenue NW, Washington, DC 20006..
~ American Gas Association
1515 Wilson Boulevard, Arlington, VA 22209.
American Lung Association
1740 Broadway, New York, NY 10019.
American Society of Heating, Refrigerating, and Air Conditioning Engineers
1791 Tullie Circle NE, Atlanta, GA 30329. -
206
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Guide to Indoor Air Pollutants
Building Owners and Managers Association
1250 Eye Street NW, Suite 200, Washington, DC 20036.
Consumer Federation of America
1424 16th Street NW, Suite 604, Washington, DC 20036.
Detail Associates, Inc.
300 Grand Avenue, Englewood, NJ 07631.
Tel: (201) 569-6708
Edison Electric Institute
1111 19th Street NW, Washington, DC 20036.
National Association of Home Builders
Technology and Codes Department
15th and M Streets NW, Washington, DC 20005.
Safe Buildings Alliance
Metropolitan Square, 655 15th Street, NW, Suite 12, DC 20005.
World Health Organization
Publication Center
49 Sheridan Avenue, Albany, NY 12210.
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Guide to Indoor Air Pollutants
Appendix I: References
ACGIH, 1984. Evaluating Office Environmental Problems. American Conference of Governmental
Industrial Hygienists, Cincinnati, Ohio.
ACGIH, 1990. Guidelines For the Assessment of Bioaerosols In the Indoor Environment, American
Conference of Governmental Industrial Hygienists, Cincinnati, Ohio.
ACGIH, 1990. Guide to Occupational Exposure Values. American Conference of Governmental
Industrial Hygienists, Cincinnati, Ohio.
ASHRAE, 1989. ASHRAE Standard -_Ventilation for Acceptable Indoor Air Qualitv_. The American
Society of Heating, Refrigerating, and Air-Conditioning Engineers, Inc., Atlanta, GA.
Centers for Disease Control of DOHH and NOISH, 1989. Indoor Air Quality - Selected References.
CDC/NIOSH, Cincinnati, Ohio.
Lippert, J., May, 1990. Im rn ovina Indoor Air. USAIR.
Morey, P. R., 1989. Bioaerosols in the Indoor Environment: Current Practices and Aagroaches
Presented at AIHA Indoor Air Quality International Symposium, St. Louis.
Morey, P. R., Indoor Air Quality. Is Your Building Sick?. Clayton Environmental Consultants, Inc.
Eller, Peter M, PhD, CIH. NIOSH Manual of Analytical Methods. 2nd and 3rd Edition. Public Health Ser
vice, Centers For Disease Control and National Institute For Occupational Safety andHealth of DHHS,
Cincinnati, Ohio.
Office of Air and Radiation, Environmental Protection Agency, 1988. Indoor Air Facts: Ventilation
and
Airuali in Offices , No.3. EPA, Washington DC.
Office of Air and Radiation, Environmental Protection Agency, 1989. Indoor Air Facts: Sick
Buildings,
No.4. EPA, Washington DC.
Office of Air and Radiation, Environmental Protection Agency, 1989. Indoor Air Facts: Environmental
Tobacco Smoke. No.5. EPA, Washington DC.
Office of Air and Radiation/Office of Research and Development, Environmental Protection Agency,
1989. Report to Congress on Indoor Air Qualitv. USEPA, Washington DC.
Office of Air and Radiation of EPA and CPSC, 1988. The Inside Story - A Guide to Indoor Air QualitX
USEPA, Washington DC., Publication No.: EPA/400/1-88/004
OSHA, 1990. OSHA Analytical Methods Manual, second edition. Occupational Safety and Health
Administration, Department of Labor, Salt Lake City, Utah.
OSHA, 1987. 4SHA Chemical Information. Manual. Occupational Safety and Health Administration,
Department of Labor, OSHA Instruction CPL2-2.43.
Sheldon, L. S., 1988. Indoor Air Quality in Public Buildings: Volume I. Office of Acid Deposition,
Environmental Protection Agency, Washington DC.
Sheldon, L. S., 1988. Indoor Air Quality in Public Buildings Volume 11. Office of Acid Deposition,
Environmental Protection Agency, Washington DC.
Detail Associates,-Inc. 209

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Guide to Indoor Air Pollutants
Appendix ff Indoor Air Quality Qestionnaire
Establishment Where Possible IAQ Problem Exists _
Your Name Tel
Address: Street
City State Zip
1. Complaints Yes No
(If yes, please check)
_ Temperature too cold
Temperature too hot
Lack of air circulation (stuffy feeling)
Noticeable odors
_ Dust in air
_ Disturbing noises
Other (please specify)
2. When do these problems occur?
~ Morning Daily
Afternoon Specific days of the week
_ All day Which day(s)
i No noticeable trend
3.Health Problems or Symptoms
Describe in three words or less each symptom or adverse health effect you experience more than two
times per week.
Example: runny nose.
Symptom #1
Symptom #2
Symptom #3
Symptom #4
Symptom #5
Symptom #6
(over)
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Do the above symptoms clear up within 1 hour after leaving work'?
Yes No
If no, which symptom or symptoms persist (noted at home or at work) throughout the week? Please
indicate by drawing a circle around the symptom number below.
Symptom: #1 #2 #3 #4 #5 #6
Do you have any health problems or allergies which might account for any of the above symptoms?
Yes No
If yes, please describe
4. Do any of the following apply to you?
Wear contact lenses
Operate video display units at least 10% of the workday
Operate photocopier machines at least 10% of the workday
Use or operate other special office machines/equipment
(Specify)
Currently taking medication
(Specify reasons)
5. Do you smoke? Yes No
6. Do others in your immediate work area smoke? Yes No
7. Your office or suite number is
8. What is your job title or position?
9. Briefly describe your primary job tasks
10. Can you offer any other comments or observations concerning your office environment?
(Optional)
Please Return the Questionnaire to:
Detail Associates, Inc.
300 Grand Avenue, Englewood, New Jersey 07650
Tel:- (201) 569-6708 Fax: (201) 569-4378
212 Detail Associates, Inc.

Guide to Indoor Ais Pollutants
Index of Indoor Air Pollutants
BACTERIA 27
FUNGI 31
BIOCIDES 33
VIRUS 35
ACETIC ACID 37
ACETONE 39
ACROLEIN 41
ALDRIN 43
ALDEHYDES 45 METHYL ACRYLATE
METHYL ALCOHOL
METHYLENE CHLORIDE
1-METHYLNAPHTHALENE
2-METHYLNAPHTHALENE
NAPHTHA 143
NAPHTHALENE 145
NICOTINE 147
NITROGEN DIOXIDE 149 133
135
137
139
141
ALK'1'L BENZENE SULFONATE 47
ALKYL ACRYL SODIUM SULFONATE
49 NONANE 151
n-OCTANE 153
AMMONIA 51
AMINES 53
AMMONIUM COMPOUNDS
55 OZONE 155
n-PENTADECANE 157
PERCHLOROETHYLENE
159
ASBESTOS 57 PETROLEUM SOLVENTS 161
ASBESTOS, ACTiNOLiTE 59 PINE OIL 163
ASBESTOS, AMOSITE 61 POLYCHLORINATED BIPHENYLS (PCBs)
ASBESTOS, ANTHOPHYLITE 63 165
ASBESTOS, CHRYSOTILE
ASBESTOS, CROCIDOLITE
ASBESTOS, TREMOLITE 65
67
69 PROPYLBENZENE 167
RADON 169
RESPIRABLE PARTICLES
171
BENZALDEHYDE 71 SODIUM CARBONATE 173
BENZENE 73 SODIUM PERBORATE 175
BENZO(a)PYRENE 75 SODIUM PHOSPHATE 177
n-BUTYLACETATE 77 SODIUM DODECYL SULFATE 179
BUTYRIC ACID 79
CARE30N 81
CARBON DIOXIDE 83 SULFUR DIOXIDE 181
TETRADECANE 183
TOLUENE 185
CARBON MONOXIDE 85
CHLORDANE 87
CUMENE 89
CYCLOHEXANE 91
CYCLOHEXANOL 93
n-DECANE 95
DIELDRIN 97
DIETHYL ETHANOLAMINE 99
DIETHYL PHTHALATE 101
DODECANE 103
ETHYL ALCOHOL 105
ETHYLBENZENE 107
1-ETHYL-2-METHYLBENZENE 109
1-ETHYL-4-METHYLBENZENE 111
FORMALDEHYDE 113
HEPTACHLOR 115
n-HEPTANE 117
HYDROGEN CYANIDE 119
KEROSENE 121
LEAD 123
LIMONENE 125
MAN-MADE MINERAL FIBERS 127
MENTHONE 129
MESIIYLENE 131
1,1,1 -TRICHLOROETHANE 187
n-TRIDECANE 189
VINYL CHLORIDE 191
m-XYLENE 193
o-XYLENE 195
p-XYLENE 197
Detail Associates, inc. 213

{ L
®ETAIL ASSOCIATES, t1VC.
ENVIRONMENTAL ENGINEERING CONSULTANTS
300 GRAND AVENUE, ENGLEWOOD, N.J. 07631
(201) 569-6708 FAX#(201) 569-4378
September 11, 1992
Ms. Loreen McAlpin
Philip Morris USA
P.O. Box 26603
Richmond, VA 23261
Dear Member of the Indoor Air Quality Task Force:
We would like to make you aware of the publication available on
Indoor Air Quality through our organization.
Attached herewith please find information on the aforementioned
publication. Trust you will find this information useful.
Thank you. Should you have any questions or require additional
information please" feel free to contact our office at your
convenience.
Sincerely yours,
DETAIL ASSOCTATFS; T.1?^.
/7
A. ,arac ewskit/
ewski/
President
SAJ/pln
encl.
New York Pittsburgh ® California

G YOU SICK!
want to assess their indoor environments and minimize
exposure to the pollutants.
"Guide to Indoor Air Pollutants" includes valuable infor-
mation on how to identify pollution sources and control
exposure. It also includes vital data on nearly 100 of the
most common indoor air pollutants, including:
Common and chemical names
Appearance and odor
Chemical and physical properties
Sources of contamination
Exposure limits and means of reducing exposure
Health hazards
References for air monitoring methods
"Guide to Indoor Air Pollutants" is a valuable source of
information for architects, designers, contractors, building
owners and managers, engineers, developers, maintenance
specialists, unions, building occupants and others who are
concerned about the quality of air they breathe.
"Guide to Indoor Pollutants" is available directly from
Detail Associates, Inc. for only $55 plus $5 for handling and
shipping charges. To secure your copy, please fill out the
order form below and return to us now.
Order Form.
Please rush my order of copies of Guide To IndoorAir Pollutants at $55 plus $5 shipping &
handling charges per copy to:
YOUR HOME AND OFFICE MAY BE
Look around you, at your walls, your desk, the floors.
Your carpets and wall coverings probably are made of
synthetic materials; your furniture may be covered in wood
and plastic laminates.
These are just a few of the comforts of your home or your
office that may be making you sick. Literally!
A growing body of scientific evidence indicates that
trapped air in tightly sealed homes, offices and other build-
ings has become seriously polluted by gases emanating
from pressed wood, synthetic fibers, common household
cleaners and other sources. The problem is widespread;
environmental analysts estimate that 30 percent of all com-
mercial buildings in the United States suffer from "sick
building syndrome:"
While many of us has heard about indoor pollution and
associated illnesses, few of us understand the nature of this
environmental threat and how to cope with it.
"Guide to Indoor Air Pollutants," compiled by the indoor
air specialists of Detail Associates, Inc., fills the need for
an in-depth guide to common indoor air pollution problems
and pollutants. A useful guide for professionals, it also
serves as an excellent reference for lay persons who
Title '
City/State/Zip Code
Signature Phone
Name -
Company
Address -
Fl I enclose check for $ for total amount due
Please return this portion to: Detail Associates, Inc., 300 Grand Avenue, Englewood, NJ 07631
Tel: (201) 569-6708 Fax: (201) 569-4378.

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