United States
             Environmental Protection
             Agency
Office of Research and
Development
Washington, DC 20460
July i, 1990
Annual Report
                                                     (V
             Research And Development
EPA
              Indoor Air
                                  V

              A Report on EPA's
              Indoor Air Research
              Program 1986 -1990
              Annual
              Report
                               '~  \\
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   A REPORT ON EPA'S INDOOR AIR RESEARCH
                  PROGRAM 1986 -1990
O> '; : -•
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er> 1%,
                         July 1, 1990
              Office of Research and Development

             U. S, Environmental Protection Agency
                              By
                      Michael A. Berry, Ph.D.
         Deputy Director, Environmental Criteria and Assessment Office
               Matrix Manager, Indoor Air Research Program
                               . ,  ',.,,* ,w»p p< ."J ;
         This document is intended for EPA review and comment only and
         not for outside distribution.

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          A REPORT ON EPA'S INDOOR AIR RESEARCH

                         PROGRAM 1986 - 1990


                                CONTENTS



                    EPA INDOOR AIR RESEARCH PROGRAM

Sara Title IV: Indoor Air Research Requirements

Research Activities, Organization, and Objectives

EPA Recommendations to Congress

Research Accomplishments

     Health Impact and Risk Assessment

     Source Characterization and Mitigation
                                             • >
     Building Studies and Methods Development

     Health Effects
     Biocontamination Assessment
                                APPENDICES
Appendix A: Indoor Air:  ORD IAQ Research and Extramural Activities

Appendix B: Indoor Air Research Program Publications and Presentations

Appendix C: Indoor Air Research Five-Year Plan (FY90-94)

Appendix D: EPA Indoor Air Research Program for Fiscal Year 1990

Appendix E: EPA Indoor Air Research Program for Fiscal Year 1991
Page



  1

  1

  2

  6

  6

  7


 10.

 12

 15

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                                TABLES



Indoor Air Research Program Resource Summary



                                FIGURES



EPA Moor Air Research Program Framework
Page





 4
                                    11

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 EPA INDOOR AIR RESEARCH PROGRAM STEERING COMMITTEE MEMBERS
Norman Childs
Environmental Criteria and
 Assessment Office
Research Triangle Park, NC

Da Cote
Health Effects Research Laboratory
Research Triangle Park, NC

Alfred Dufour
Environmental Monitoring
 Systems Laboratory
Cincinnati, OH

Ross Highsmith
Atmospheric Research and Exposure
 Assessment Laboratory
Research Triangle Park, NC   ..

W. Gene Tucker
Air and Energy Engineering
 Research Laboratory
Research Triangle Park, NC
In addition, there were several Agency scientists who also contributed to this report.  Of specific
note were the contributions of:  Bruce A. Tichenor,  Air and Energy Engineering Research
Laboratory; Ronald Rogers, Health Effects Research Laboratory; and William Ewald and Beverly
Comfort, Environmental Criteria and Assessment Office.

Technical Assistance

Project Management, editing, production and word processing from NSI, Inc., under contract
to the Environmental Criteria and Assessment Office, Office of Health and Environmental
Assessment:  Miriam Gattis, Lynette Davis, Phil Gagne, Derrick Stout and Jorja Followill.
                                        ill

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                     EPA INDOOR AIR RESEARCH PROGRAM
SARA TITLE IV: INDOOR AIR RESEARCH REQUIREMENTS
In October 1986, Congress passed the Superfund Amendments and Reauthorization Act (SARA,
PL 99-499). The Act included the Radon Gas and Indoor Air Quality Research Act (Title IV),
which for the first time mandated a federal indoor air research program. Under this legislation,
EPA is directed to undertake a comprehensive effort of research and development, including the
coordination of government and private efforts.  The ultimate goal of this activity is to
characterize indoor air nationwide, predict health consequences, and disseminate information to
the public regarding indoor air control techniques and mitigation measures.
                          i
Research program requirements under SARA include:  identifying and assessing the sources and
levels of indoor air pollution; developing instruments for indoor air quality data collection; and
studying complaint buildings.  The statute also requires research directed at identifying effects
of indoor air pollution on human health.  In the area of mitigation and control the following are
required: developing mitigation measures to  prevent or abate indoor air pollution; developing
methods to reduce or eliminate indoor air pollution; developing methods to assess the potential
for contamination presented by new construction; and examining design measures to improve
indoor air quality.

RESEARCH ACTIVITIES. ORGANIZATION. AND OBJECTIVES

In October  1986,  EPA's Office  of Research and Development (ORD) established a matrix-
managed research  program  that  emphasizes  risk  assessments  for indoor environments,
development of sampling devices for use indoors, indoor air quality models, materials testing
methods, research test house experiments, and investigations of special complaint buildings.  In
conducting  indoor air research, the Office of Research and Development  has integrated the
research efforts of the  Health Effects  Research Laboratory, the Atmospheric Research and
Exposure Assessment Laboratory, the Air and  Energy Engineering Research Laboratory, and the
Environmental Criteria and Assessment Office all located at Research  Triangle Park, NC, and
more recently, the Environmental Monitoring Systems Laboratory in Cincinnati, OH. A research
steering committee has been  formed  consisting of a  senior research  manager from  each
laboratory.  The committee advises the  matrix manager on specific research projects, resource
requirements and  allocation, and assists in coordinating multidisciplinary  research projects.
Appendix A lists all the major indoor air research activities in the  Office of Research and
Development and the individuals responsible for each activity.

The Office of Research and Development's Indoor Air Research Program has strived to support
the needs of EPA's emerging Indoor Air Division, Office of Air and Radiation (OAR), as well
as the technical needs of state and local  government agencies and private sector

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organizations.  EPA's researchers have taken the lead in working with other Federal agencies to
identify the most important indoor air quality concerns. The Agency's 1989 Report to Congress
outlines the most important research needs of government and the private sector. EPA's Indoor
Air Research Program is addressing twenty-four of the thirty-three priority research needs
identified in the report to Congress.

Subsequent to the submission of the Agency's report to Congress, EPA designed a long term
program and strategy that will play a major role in addressing indoor air needs. Appendix C
outlines ORD's 5-year plan for  indoor air research.  That plan, along with individual project
descriptions of indoor air research projects, was presented to other Federal agencies in indoor air
research through the interagency Committee for Indoor  Air Quality (CIAQ) in January 1990.
Also, since January 1990, the Indoor Air Research Program has conducted a survey of ongoing
indoor air research throughout the United States.  The results of that survey will appear in a
separate report that will be presented to the CIAQ and the EPA Science Advisory Board in the
near future.  In the 1989 Report to Congress, EPA made six recommendations intended to
develop the necessary information required by Title IV of SARA. These recommendations are
listed below. They represent the primary  objective, activity, and support areas of the Indoor Air
Research Program.

EPA RECOMMENDATIONS TO CONGRESS

      1.    Research to better'Characterize exposure  and  health  effects  of chemical
           contaminants and pollutant  mixtures  commonly  found indoors  should  be .
           significantly expanded.

     2.    A  research program to characterize and develop mitigation  strategies for
           biological contaminants in indoor air should be developed.

     3.    Research to identify and characterize significant indoor air pollution sources and
           to evaluate appropriate mitigation strategies should be significantly expanded.

     4.    A program is needed to develop and promote, in conjunction with appropriate
           private sector organizations,  guidelines covering ventilation, as well as other
           building design, operation, and maintenance  practices for ensuring that indoor
           air quality is protective of public health.

     5.    A program of technical assistance and information dissemination, similar in
           scope to the Agency's radon program, is needed to inform the public about
           risks and mitigation strategies, and to assist state and local governments and the
           private sector in solving indoor air quality problems. Such a program should
           include an indoor air quality clearinghouse.

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     6.    The Federal government should undertake an effort to characterize the nature
           and pervasiveness of the health  impacts associated with indoor air quality
           problems in commercial and public buildings, schools, health care facilities,
           and residences, and  develop and  promote  recommended  guidelines for
           diagnosing and controlling such problems.
These recommendations are based on identified potential indoor air hazards throughout the
Nation as well as the need to inform the public of effective control measures and mitigation
procedures.  Along with radon, the health impact from exposure to biological pollutants and
environmental tobacco smote (ETS) is quite substantial.  There is enormous public concern
over, exposure to and the effects of many of the gas phase organic compounds found indoors.
This has led to a growing demand to study the phenomenon of "chemical sensitivity" in humans.
Previously, little research has been directed towards identifying the cause of complaints in
buildings.  To date,  no advances  have been  made in explaining the  differences between
noncomplaint and complaint buildings.

To accomplish the research objectives identified in the report to Congress, ORD has organized
and grouped projects and activities in the following areas:                        _

       •   Indoor Air Program Management and Technology Transfer

       •   Indoor Air Health Impact and Risk Assessment
       •   Indoor Air Source Characterization and Mitigation

       •   Indoor Air Building Studies and Methods Development
       •   Indoor Air Health Effects

       •   Biocontamination Assessment

The general goals and direction of each of these research areas are presented in the five year plan
shown in Appendix C.  The specific projects carried out and planned under these areas for FY90
and FY91 are shown in Appendices D and E, respectively.  Table 1 presents the funding history
of the research program since FY87.

The Indoor Air Research Program addresses a complex environmental problem requiring the
successful  integration  of  different  disciplines  and  technical  activities  (risk  assessment,
engineering, methods development, health effects research, field studies, and microbiology).
Figure 1 illustrates the major research project areas of the Research Program. In relation to each
other, these information gathering activities form the  research program framework.  Their
ultimate purpose is to provide the public with technical information

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TABLE 1. INDOOR AIR RESEARCH PROGRAM RESOURCE SUMMARY
Research Area

IA Assessment
Building Studies
Health Effects
Source Assessment and Control
Biocontamination Research
TOTAL

IA Assessment
Building Studies
Health Effects
Source Assessment and Control
TOTAL
»
IA Assessment
Building Studies
Health Effects
Source Assessment and Control
TOTAL

IA Assessment
Building Studies
Health Effects
Source Assessment and Control
TOTAL
IA Assessment
Building Studies
Health Effects
Source Assessment and Control
TOTAL
FTE
FY91
3.0
3.0
5.0
7.0
JLQ
17.0
FY90
3.0
3.0
1.0
_AQ
15.0
FY89
3.0
3.0
1.0
8.0
15.0
FY88
3.0
3.0
1.0
8.0
15.0
2.0
3.0
1.7
6.0
12.7
S&E
(SK)

308.0
299.4
310.0
881.7
•_•—
1551.1

174.4
226.1
60.2
904.3
1365.0

180.0
181.5
61.1
538.4
961.1

180.0
174.0
100.0
398.0
852.0
0
210.0
100.0
320.4
630.4
R&D
($K)

467.0
1313.5
841.6
1579.8
200.0
4401.9

238.6
564.4
949.1
823.8
2575.9

249.0
616.0
960.0
921.2
2746.2

299.0
533.0
625.0
840.0
2297.0
178.0
767.0
550.0
725.0
2220.0
Total
<$K)

775.0
1612.9
1151.6
2461.5
200.0
6201.0

413.0
790.5
1009.3
1728.1
3940.9

' 429.0
797.5
1021.1
1459.6
3707.2

479.0
707.0
725.0
1238.0
3149.0
178.0
977.0
650.0
1045.4
2850.4

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on the. health risks of poor indoor air quality and at the same time give guidance for the
attainment and maintenance of healthy indoor air.

During the FY86-89 period, ORD's research strategy for indoor air was to develop the necessary
equipment and experience by which to assess indoor air quality. The program emphasized the
development of source assessment and testing methods, indoor air models, monitoring methods,
test house procedures, and risk assessment methodologies. Since then the program has begun to
demonstrate a capability to measure human response in a clinical research setting and to conduct
large building studies, such as in the Library of Congress and EPA's headquarters building
studies in Washington.

In addition, the research  program is developing animal  test capabilities to assess multiple
pollutants from indoor sources, enlarging the building studies program, planning a mitigation
guidance component of the program, and it is beginning preliminary testing on a limited number
of air cleaning devices.  The risk assessment component of the program has begun to develop
methods for assessing multiple pollutants and noncancer endpoints. A biocontaminant assessment
component of the Research Program will be initiated in  FY91.

RESEARCH ACCOMPLISHMENTS

Appendix B presents the  numerous publications of and presentations by EPA's indoor air
researchers. These efforts have clearly contributed to a better understanding of indoor air quality
and its impact on public health.  Several researchers have been recognized as national experts
in their specialty areas and many of them continue to perform as leaders in both national and
international research activities.   The major accomplishments of EPA's Indoor Air  Research
Program  and its on-going research are summarized below. These accomplishments are reflected
in the several manuals and fact sheets either in preparation or already released to the public
through OAR's Indoor Air Division.

Health Impact and  Risk Assessment

•    An  information assessment identifying the hazards of indoor environments was completed
     in 1987 and submitted to Congress as part of EPA's Indoor Air Quality Implementation
     Plan.  The document serves as the first step in the process of risk assessment in that it
     provides a preliminary hazard identification of indoor pollutants.  The assessment also
     discusses the  known monitoring methods and mitigation techniques.

•    A comprehensive bibliographic data base (Reference Bibliography) for indoor air pollution
     has been established.  The citations of all  indoor air research publications known to EPA
     are  published yearly.  The Reference Bibliography is an ongoing project that is intended to
     be a complete list of all published information pertaining to indoor air pollution. Health
     effects,  monitoring methods, exposure levels, mitigation techniques, office building, and
     specific individual pollutants are some of the key word categories that can be searched in

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     the bibliographic data base.  This project is useful to Federal, state, and local agencies,
     researchers, and private companies who are interested in determining what information has
     been published in a specific area of indoor air pollution. The bibliographic data base is
     available in both computerized and published versions.

•    A  risk assessment methodology  is being developed and tested for its  effectiveness in
     representing the risk from exposure to multiple pollutants from products such as carpet,
     tobacco and unvented kerosene heaters.

•    Several reports have been completed under an especially established Indoor Air Research
     Report Series to highlight the results of the Indoor Air Program.  These reports are
     undergoing Office of Health and Environmental Assessment (OHEA) review and include:
     Development of a Risk Characterization Framework, A\Review of Indoor Air Quality Risk
     Characterization Studies, Methods  of Analysis for Environmental Carcinogens, Indoor
     Concentration of Environmental Carcinogens, Use of Benzene Measurement Data in Risk
     Characterization Estimate: A Preliminary Approach.

•    Other reports are being prepared that address subjects such as the health impact associated
     with the stress and annoyance of odorous compounds and the health consequence of cleaning
     and maintenance practices in the indoor environment.

Source Characterization and Mitigation

•    Laboratory studies of the emissions from unvented kerosene space heaters identified many
     vapor- and particulate-phase organic compounds,  plus acid aerosols, that are of potential
     health concern.  (The subsequent section on health effects contains further information of
     the results of these studies.)  Testing results are being summarized and factors important
     in  kerosene heater selection and use are being reported as input to EPA guidance.

*    Testing procedures for evaluating the emission characteristics of building materials and
     consumer products have been developed.  Small test chambers are used to determine the
     emission rate and  composition  of  vapor phase organics emitted from  indoor  sources.
     Research is conducted to evaluate the effect of temperature, relative humidity, air exchange
     rate, and product loading on the emission  rates.  A variety of sources have been tested
     including polyurethane coatings,  wood wax, architectural coatings, moth repellant (para-
     dichlorobenzene), dry cleaned  fabrics (tetrachloroethylene), air fresheners,  carpet,  and
     office partitions.

»    An international interlaboratory comparison study is underway to develop statistics on the
     comparability of chamber test data.  The study is being jointly undertaken by EPA and the
     University of Aarhus (Denmark) and includes participants from the United States, Denmark,
     Sweden, West Germany, and Italy.

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EPA has drafted a Standard Guide for small chamber testings for acceptance and publication
by the American Society for Testing and Material (ASTM).   The Guide has passed
subcommittee balloting and is being voted on by the Society's full committee.   It is
anticipated that balloting by the full Society will occur later this year.  A version of the
Guide has been published as an EPA report (EPA 600/8-89/074)  and has been widely
distributed for use by both IAQ researchers and private sector manufacturers of indoor
materials and products.

Through its program to characterize sources of indoor air pollutants, EPA has introduced
the concept  of controlling low-emitting  indoor materials and products as an important
approach  to pollution prevention and  indoor air quality  control.   Several major
manufacturers  are now using procedures developed under EPA's indoor air research
program to test emissions and predict indoor exposures from their products.  This is a
significant step toward private-sector involvement in improving indoor air quality.

Fundamental research on the behavior  of indoor sinks has been initiated.   Rates of
adsorption to and desorption from carpet, drywall, ceiling tile, upholstery, and glass have
been determined for ethylbenzene and tetrachloroethylene via  small test chamber studies.
Indoor air research test house studies have shown that reemissions (desorption) from  sinks
have a major impact on the long-term exposure to pollutants from indoor sources. The new
data on  sinks will  greatly increase our ability to predict indoor pollutant concentrations
through modeling, and may help explain occupant complaints in buildings with no^apparent
sources-of pollutants.     .                                       •         '

Exposure  to emissions from indoor sources  can  be controlled by appropriate source
management and proper ventilation.  ORD has applied these concepts  to several indoor
sources  of concern to EPA Program Offices by using data obtained  in small chamber and
test house studies.  "Airing out" freshly dry cleaned  clothes as a means to reduce indoor
exposure to tetrachloroethylene was shown to be ineffective, due  to the slow decay of
tetrachloroethylene emissions (study conducted for Office of Toxic Substances and OAR).
Appropriate conditioning of carpet for 30 days prior  to installation can reduce indoor
concentrations of 4-phenylcyclohexane (4-PC) to below 1 ppb  (study conducted for the
Office of Administration). Recommendations were made for the time between application
of an architectural coating and an adhesive in an office and the return of the occupants
(study conducted for Project 1992 and the Environmental Health and Safety Division, Office
of Administration).

The indoor air research test house has been used for the study of pollutant sources, sinks,
and transport of pollutants under scenarios that would  be expected to be encountered in
homes.  Several products from which organic emissions have been studied include:  moth
crystals, (invented kerosene space heaters, solvent emissions from dry cleaning of clothing,

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aerosol spray products and other products that are applied wet and then allowed to dry on
site, oil wood  stain, varnishes, and floor waxes.  Several studies on air movement in a
house provided information on how pollutants move and how changes can be made to
modify these movements. For example, the fan of the heating/cooling system of a home
completely overcomes any effect of area fans, such as bathroom and/or kitchen fans.
However, if the heating/cooling fan is turned off, the small fans can reduce pollutant levels
in the closed rooms they are ventilating. Future work in the test house will explore:  1) the
effects of pressure and  temperature on the movement of pollutants;  2) other organic
emissions from consumer products; and 3) changes in products and uses that can reduce
exposure to inhabitants.
                          i
Analytical methods developed by EPA for indoor air research that are appropriate for
general use are being rewritten in ASTM format for publication in the ASTM Books of
Standard Methods.  The canister collection method for volatile organic compounds is in the
process now.

Research on indoor air control methods has examined the effectiveness of activated carbon
for control of low concentrations of  vapor-phase organics.   These  studies show that
activated carbon devices  are ineffective in removing the vapor-phase organic compounds.
Alternative mechanisms for removing low concentrations of vapor-phase organics are being
evaluated on a theoretical basis.

The emission of ozone from electrostatic precipitator air cleaners has been evaluated. The
study show that large in-duct electrostatic precipitator air cleaners can generate ozone.
Additional experiments are planned to determine the destruction of ozone in ductwork and
in normal indoor environments.  Experiments will  also be conducted to determine the
effectiveness of carbon beds and catalytic beds in preventing ozone from entering the living
spaces.

Preliminary experiments on  the effectiveness of  particulate air cleaners have  been
completed. These experiments demonstrate the need for particle size-based testing of air
cleaners because, with existing methods, filters with high ratings were less that SO percent
efficient in removing particles in the size range of environmental tobacco smoke.  An
improved test method is  being developed and evaluated in FY90.  Work to assist private
standard setting bodies such as ASHRAE in developing standard methods for evaluating air
cleaners based on this research is underway.

Cooperative research with ASHRAE to determine definitions of and methods for evaluating
ventilation effectiveness  is underway.  A workshop to develop ventilation effectiveness
definitions, methods, and research needs was held in the fall of 1989. This meeting brought
together the leading researchers and practitioners in the ventilation field.  The output of the
workshop will assist  private organizations  such as  EPRI  and ASHRAE as  well as
government organizations conducting research in ventilation.

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•    A preliminary test method for evaluating the particulate emissions from vacuum cleaners
     has been developed. The preliminary tests show that vacuum cleaning may be a significant
     source of respirable particles in indoor air, at least for short periods of time.  Several
     private companies have expressed interest in the results of this work and in working with
     EPA to develop a standard test method.

*    The indoor air quality model has been verified in several experiments conducted in the EPA
     indoor air test house.  The model makes it possible to use the source emission rate data
     collected in chamber studies to predict the impact of various sources on indoor air quality.
     The model shows the impact of reemitting  sinks and has proven valuable in evaluating
     indoor air quality control options. The model has been revised to make it easier for the
     less-expert user to use.  Additional research  is revising  the  model to predict  personal
     exposure to pollutants from indoor sources. Work is also underway to better define room-
     to-room air flows, infiltration of outdoor air, and imperfect mixing on indoor air quality.
     The model has  already proved to be a valuable tool for people involved in indoor  air
     research and practice. Over 200 copies of the model have been distributed.

•    A Database of Indoor Air Pollutant Sources (DIAPS) has been developed and there have
     been many requests for the data base from both foreign and domestic researchers.  The data
     base is being distributed on a limited basis to get user response.  The basic structure of
     DIAPS has been changed to reflect user concerns on speed and to make user update easier.
                                                      •
Building Studies and Methods Development

*    A compendium  of methods for measuring indoor air pollutants and a technical assistance
     document have  been  compiled to provide standard operational procedures and technical
     assistance to agencies and individuals  responsible  for sampling and assessing indoor air
     quality.  This methods compendium contains technically-reviewed sampling and analysis
     procedures in a standardized format for measurements of selected indoor pollutants of
     primary importance.  The ten chapters of the compendium cover determination of volatile
     organic compounds (VOCs), nicotine, carbon monoxide, carbon dioxide, nitrogen dioxide,
     formaldehyde, benzo(a)pyrene and other polynuclear aromatic hydrocarbons, acid gases
     and aerosols, particulate matter, pesticides, and air exchange rates.  Each chapter contains
     one or more active or passive  sampling procedures along with one or more appropriate
     analytical procedures. Abbreviated versions of each method are also being developed for
     use by field operators and laboratory analysts.

•    Passive samplers and personal monitoring devices have been  developed for VOCs,
     formaldehyde, ozone, and nitrogen dioxide.  Research is underway to develop passive and
     personal devices for carbon monoxide and ozone.  Passive  samplers are important because
     they are of low  cost,  can be worn on a person's clothing, and can be used as a screening
                                          10

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tool to indicate areas with highest pollutant concentrations.  Passive personal devices or
badges are important because they are low cost, unobtrusive, and require minimal resources.
They also nay provide a better estimate of personal exposures.  Passive badges do have a
shortfall in monitoring and analytical sensitivity and accuracy when compared to the routine
active sampling techniques. However,  the are good screening tools to determine locations
for additional monitoring or compliance.  Changes in pollutant levels can be measured by
personal  monitoring devices as the wearer moves into and out of a room containing a
combustion appliance or humidifier in use. Measurements can also be gathered from small
microenvironments such as within a car, parking garage, or dry cleaning establishment.
Exposures can be examined during personal activities, such as cleaning, stripping furniture,
or after new furnishings have been installed in a home or office.  These samplers are used
to more accurately predict exposure scenarios where high pollutant levels may be present.

Research has been initiated to develop sampling and analytical methods for VOCs,
semivolatile organic compounds (SVOCs), and aldehydes.  Multiple species from these
classes of compounds are routinely observed in varying concentrations indoors.   Sources
for the compounds include furnishings, combustion appliance  emissions, glues, paints,
solvents, and other products for indoor use. Particular emphasis is being placed on the
collection and analysis  of  polar VOCs/SVOCs, as  these compounds  are commonly
associated with health implications, including cancer and neurotoxic effects.

A sampling method has been developed to measure peak exposure of VOCs that may result
from personal activities.  Initial studies examined  the effects of cleaning and painting,
combustion sources, water off-gassing, and automobile exhaust  emissions. This research
is important because  other sampling methods are unable to delineate the peak pollutant
levels that may have serious health consequences.

The EPA, in collaboration with DOE and NIST, has supported the development of an
advanced mathematical  model to predict indoor air pollution concentrations in multiroom
buildings. A user-friendly interface, entitled CONTAM87, is being designed for use with
the model. CONTAM87 is a general purpose contaminant dispersal model for predicting
concentration levels within a multizone complex. The model requires as input specification
of the mass flow rates between the zones.

Development of an indoor air quality model has also been undertaken by EPA engineers.
The first version of  a  model designed to simulate pollutant interactions in the indoor
environment has been published. Experiments in the indoor air  test home have confirmed
the model predictions for a limited range of conditions.  This model will be an invaluable
tool for  understanding  indoor air quality problems especially  in smaller buildings and
residences. The effects of sources, sinks, inter-room air flow, and HVAC systems can be
examined through the model. It will help researchers evaluate indoor air quality problems
and solutions and aid in building design.
                                     11

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     Research is evaluating  portable home humidifiers and examining the processes  and
     mechanisms that result in the aerosolization into indoor air of impurities in the charging
     water.  The research is designed to characterize the chemical and physical characteristics
     of the humidifier-generated aerosol and assess the health implications resulting from typical
     exposures.

     EPA, along with DOE and NIOSH, is investigating complaints of indoor air pollution in
     the Library of Congress.  EPA will conduct air monitoring analysis in that building and
     work with  health scientists of other  agencies to explain health effects associated with
     pollution concentrations.

     EPA researchers have responded to  the immediate needs of their own agency  in the
     investigation of complaints in EPA Headquarters, Washington, DC.  Extensive air samples
     have been taken, materials (carpet) have been evaluated, and a report on sampling results
     has been submitted to EPA management.

     Technical guidance documents  are being developed for sick building syndrome (SBS)
     investigators.  Step-by-step procedures are being established to allow investigations to
     follow a logical progression and to enable comparison between studies.

     Research is being conducted to develop a standardized building diagnostic and assessment
     protocol.   Studies are being planned to collect baseline data from  noncomplaint and
     complaint buildings that can be used by indoor air quality investigators to assess the indoor
     air quality in large buildings. The indoor air quality in selected office buildings will be
     monitored to evaluate temporal and spatial distributions of indoor air contaminants and to
     relate the indoor air quality to worker discomfort symptoms.
Health Effects
     Public interest in indoor air pollution and complaints of sick building syndrome have
     increased  rapidly during the past few  years.  VOCs have  been identified as major
     constituents of indoor air pollution and the health effects of exposure to these chemicals are
     of considerable concern. Danish studies suggest that human exposure to a complex mixture
     of VOCs (25 mg/m3), representative of chemicals and concentrations found in new homes,
     produces sensory irritation  and impairment of short-term memory.   EPA  research has
     confirmed that exposure to the Danish mixture produces sensory irritation in normal, health
     young adult males (a subset of the general population least likely to show such effects), but
     no evidence of memory deficit or other behavioral impairments was found.  Further studies
     of chemically sensitive individuals are planned to clarify these findings.  Studies using VOC
     mixtures more representative of American buildings are also planned.
                                          12

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In a second study, nasal lavage was performed to assess inflammatory response in the upper
airways using the same mixture and concentration. Evidence of an inflammatory response
(increased numbers of polymorphonuclear leukocytes  (PMNs)) was  found following
exposure to VOCs compared to clean air. This rinding is very important as it suggests that
PMNs may provide a useful biochemical marker to identify chemically sensitive individuals
and to characterize sick building syndrome.
                    i
Additional studies, using animal and in vitro systems, are being initiated to assess the
potential  health  impact of VOC mixtures  on selected organ systems, e.g.,  immune,
respiratory, nervous, and/or reproductive, as well as the potential mutagenicity. Results
will be compared to information collected in human studies in order to develop models for
animal-to-human extrapolation and also to help guide additional human studies.  Based on
existing evidence of respiratory tract inflammation following controlled VOC exposure, and
complaints of increased respiratory disease as a component of the Sick Building Syndrome,
initial research will focus on the evaluation of immunotoxic effects and assessment of
respiratory initancy following controlled VOC exposures in inhalation chambers. Elevated
ambient levels of inhaled air pollutants have been associated with an increased susceptibility
to respiratory  viral  infections, particularly  in children.  The socioeconomic impact of
influenza viral disease is estimated at  3-5 billion dollars per year in the United States.
Furthermore, viral upper respiratory tract infection has been implicated as an important
contributor to the etiology of asthma, the incidence and mortality of which is increasing in
the United States.  Studies will be performed to determine whether indoor air pollutant
mixtures  affect the susceptibility or  severity of airway hyperreactivity  in the influenza-
induced model for asthma. A new animal inhalation facility, which is nearing completion,
will be used  to  fulfill experimental  designs that address simple and complex exposure
toxicology as well as aim at dissecting  questions of additivity or interaction of VOCs in a
conceptual framework to  develop generic approaches to further mixture study.  Also, in
collaboration  with AEERL, offgas VOC initancy and mutagenicity can be assessed to
determine acute effects of exposure on  breathing patterns as a bioassay system for relative
potency as well as potential carcinogenicity of these gases or combinations.

Environmental tobacco smoke (ETS) is the largest source of indoor air pollution and is also
the major combustion source  contributing  to total human exposure to  mutagens and
carcinogens.   ORD  studies provide  specific data on human exposure  to ETS using
biochemical and  mutagenesis bioassay  measures as well as physical chemical markers of
exposure. Controlled laboratory chamber  studies determined ETS emission factors for
mutagenic activity using  Salmonella mutation assays.  The emission factors for alkenes
(e.g., 1,  3-butadiene) and  aldehydes (e.g., formaldehyde), which are either known or
potential carcinogens, are also being investigated for the first time in these studies. Human
exposure concentrations and dosimetry are  assessed and compared under both controlled
chamber and actual indoor environmental conditions. Levels of nicotine and its major
                                     13

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metabolite, cotinine, have been found  to be useful quantitative and semiquantitative
measures of human exposure and dosimetry.  The relationship between nicotine exposure
and urinary cotinine excretion has been studied in preschool children exposed in their homes
and in adults exposed on commercial airline flights. Air monitoring studies in residences
and public indoor areas using both nicotine and mutagenic activity have demonstrated that
separation of smokers into separate areas does not achieve an ETS-free  or genuine
nonsmoking area unless there is both physical separation and separate ventilation. The data
from  these studies provide information needed in developing policy and guidance
information that will be provided to the public, local, state, and national governmental
agencies and other specific groups (e.g., ventilation engineers, etc.) on how to improve
indoor air quality.

Combustion sources are significant sources of pollutants in homes. Since 1983, ORD has
investigated the health effects of indoor combustion emissions on human health in support
of the Clean Air Act.  A major component of this ORD effort has been the investigation
of lung cancer and indoor air pollution from (invented coal and wood combustion in homes
in a rural county, Xuan Wei,  in China under a China-U.S. Protocol for Scientific and
Technical Cooperation in the Field of Environmental Protection.  This Xuan Wei Project
has been described as a landmark and EPA's single most important joint research project
with China. ORD scientists and Chinese scientists jointly investigated the etiology of lung
cancer,  using an interdisciplinary, approach to link air monitoring, chemical, physical and
lexicological data to human epidemiological data.  This study showed a strong association
between indoor air pollution and lung cancer, and also identified the classes of compounds
associated with incidence of lung cancer.  This study represents a major contribution to the
understanding of nontobacco-related environmental causes of lung  cancer in man, and
demonstrated the difference in  cancer risk that results from variations of the type of coal
and wood combustion emissions.  It also provided a unique opportunity to use a human
population with high exposures and health effects to apply and validate the biomarkers,
which had been developed in the laboratory. Further, sampling needs for this study led to
the development of a medium volume sampler to collect PM10 and semivolatile organics.
Since its development, it has been widely used on other EPA programs, including the IACP
and indoor air projects on kerosene heaters and environmental tobacco smoke.

An estimated  15-17 million unvented kerosene heaters have been sold in the United States.
Many of them  were sold to the residents of mobile homes and multi-dwellings.   The
pollutants emitted from kerosene heaters can accumulate in homes with small air volume
and low ventilation.  Studies were conducted both in a chamber  and in mobile homes to
characterize the kerosene heater emissions for mutagenicity and chemical constituents and
to assess the  human exposure  in a real home environment.  Both the chamber and the
mobile home  studies show that kerosene heaters emit fine respirable particles that contain
mutagenic organic pollutants, including carcinogenic polycyclic aromatic
                                     14

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     hydrocarbons (PAH) and nitro-PAH. High mutagenic activity was found during the start-
     up stage. High emissions of SVOCs from kerosene heaters were found in both the chamber
     and the home studies.  Limited health effects information is available on the SVOCs and
     further work is characterizing them.  The home study also shows that, as a result of
     kerosene heater usage in homes, the PM10 and CO concentrations in three homes (out of
     a total of eight homes monitored) exceeded the United States National Ambient Air Quality
     Standards, including two homes that exceeded the PM10 24-hour standard and one home
  ••   mat exceeded the CO 1-hour peak and 8-hour average standards.  These data suggest that
  \   the emissions from unvented  kerosene heaters  impact  air quality in homes  and can  be
  ;   potentially carcinogenic.

Bibcontamination Assessment

•    Recently it has become obvious that exposure to biological pollutants, i.e., mold, mold
     spores, mildew, bacteria, viruses, and insect and animal parts and excreta, poses an adverse
     effect on human health in the indoor environment.  A preliminary report on the potential
     health impact of the pollutants is being prepared, and is scheduled to be completed within
     the next few months.   This report will also summarize the occurrence and sources of
     biological contaminants in the indoor environment. The health effects to be studied include
     the pathogenicity, allergenic potential, and  toxicity of the biological pollutants. This report
     will also discuss the sampling methods available to date, and will review the research
     needed to gain an adequate understanding of the impact of biological pollutants. When
     possible, the allergenic, immunogenic, and immunotoxic potential of these pollutants will
     also be quantified  so that a correlation can be  made between concentration  and disease
     potential.   A more comprehensive report on biological contaminants  in the indoor
     environment is expected to be completed in FY91.

•    A  major problem in identifying  and characterizing effects from exposure to biological
     contaminants in the indoor  environment is the lack of  standardized  detection and
     identification methods.  To this end, the Environmental Monitoring Systems Laboratory-
     Cincinnati is developing methods to greatly  improve the standard sampling and measurement
     methods for pathogens and allergens indoors. The laboratory will also work to characterize
     sources of indoor microbial contamination and define the relationship between indoor air
     quality, infections, and allergies.  The program will initially  focus on the development of
     optimum detection methods for bacteria and fungi. Concurrently, the collection fluid  for
     impinger type samplers will be modified to minimize the holding time after impingement.
     Methods for critical factors, such as, virulence and allergy determinants, will be developed.
     Critical factors are specific characteristics of microbes that confer on them the ability to be
     pathogenic or allergenic.  Fungi  associated with indoor air environments are difficult to
     identify because identification usually is based on morphological characteristics that require
     the skills of a highly trained mycologist.   This process will be simplified by
                                          15

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developing a series of gene probes for those fungal species most frequently isolated from
indoor air environments. The methods development phase of the program will be Mowed
by an evaluation phase wherein the methods will be tested under field conditions, i.e., in
the indoor  air environment.  This will be accomplished by identifying various types of
contaminated  indoor  environments, sampling  the air in  those  environments, and
characterizing and quantifying the exposure factors.   During this period the exposure
assessment methods will be standardized and quality assurance protocols will be developed.
During the evaluation phase various sites will be examined to determine if they can be used
to establish the relationship between indoor air quality, as measured by critical factors and
the response of individuals after exposure to pathogens or allergens.
                                     16

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APPENDICES

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APPENDIX A

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               INDOOR AIR:
ORD IAQ RESEARCH AND EXTRAMURAL ACTIVITIES



                JULY 1, 1990

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APPENDIX B

-------
 INDOOR AIR RESEARCH PROGRAM
PUBLICATIONS AND PRESENTATIONS

          JULY 1, 1990

-------
  INDOOR AIR RESEARCH PROGRAM PUBLICATIONS AND PRESENTATIONS
                          CONTENTS
PUBLICATIONS AND PRESENTATIONS FROM THE AIR AND
ENGINEERING RESEARCH LABORATORY'S INDOOR AIR PROGRAM
Page


  1
PUBLICATIONS AND PRESENTATIONS FROM THE ENVIRONMENTAL
CRITERIA AND ASSESSMENT OFFICE'S INDOOR AIR PROGRAM
  17
PUBLICATIONS AND PRESENTATIONS FROM THE ENVIRONMENTAL
MONITORING SYSTEMS LABORATORY'S INDOOR AIR PROGRAM
  21
PUBLICATIONS AND PRESENTATIONS FROM THE HEALTH
EFFECTS RESEARCH LABORATORY'S INDOOR AIR PROGRAM
  28

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   PUBLICATIONS AND PRESENTATIONS FROM THE AIR AND
2NERGY ENGINEERING RESEARCH LABORATORY'S INDOOR AIR
                                       PROGRAM


 PUBLICATIONS
 Blackard, A. L. (1987) Automation of an emissions testing facility.  Atmos. Environ. 21: 355-357.

 Boone, P. M.; Leaderer, B. P.; White, J. B.; Hammond, S. K. (1988)  Chamber studies characterizing organic
       emission from unvented kerosene space heaters:  Phase n.  In:  Proceedings of the 1988 EPA/APCA
       international symposium on measurement of toxic and related air pollutants. EPA 600/9-88-015.

 Brennan, T.; Pyle, B. E.; Williamson, A. D.; Bdzer, F. E.; Osborne, M. C. (1989)  Fan door testing on crawl
       space building. In:  Proceedings of the ASTM symposium on air change rate and air tightness in buildings,
       Atlanta, GA.

 Carretti, J. (1988) Radon Mitigation follow-up and long-term monitoring. U. S. Environmental Protection Agency,
       Air and Energy Engineering Research Laboratory, Research Triangle Park, NC  EPA 600/7-88-005.

 Clayton, R. K.; Stepenson, E. E.; Jackson, M. D.; Sparks, L. E. (1988) EPA's indoor air quality test house:
       3. Moth cake studies. In:  Proceedings of the 1988 EPA/APCA symposium on measurement of toxic and
       related air pollutants. EPA 600/9-88-015.

 Crum, J. M. (1986) Source emissions database for indoor air pollution. U. S. Environmental Protection Agency,
       Air And Energy engineering Research Laboratory, Research Triangle Park, NC.  EPA 600/9-86-013.

 Dunn, J. E. (1987) Models and statistical methods for gaseous emission testing of finite sources in well-mixed
       chambers. Atmos. Environ. 21: 425^*30.

 Dunn, J. E.; Henschel, D. B. (1987) Statistical aspects of autoregressive  models in the  assessment of radon
       mitigation.  In:  Seifert, B.; Esdorn, H.; Fischer, M.; Rueden, H.; Wegner, J., eds., Indoor air '87:
       Proceedings of the 4th international conference on indoor air quality and climate, v. 2, environmental tobacco
       smoke, multicomponent studies, radon, sick buildings, odours and irritants, hyperreactivities and allergies,
       August, Berlin, Federal Republic of Germany. Institute for Water, Soil and Air Hygiene; pp. 329-334.

 Dunn, J. E.; Tichenor, B. A. (1988) Compensating for sink effects in emission test chambers by mathematical
       modeling. Atm. Environ. 22(5):  885-894.

 Ensor, D. S. et al. (1988) Air cleaner technologies for indoor air pollution. In:  Engineering Solutions to Indoor
       Air Problem, Proceedings of the ASHRAE conference IAQ '88.

 Findlay, W. 
-------
Gadsby, K. JT. et al. (1988) Rapid Diagnostics:  Subslab and wall depressurization systems for control of indoor
       radon. U. S. Environmental Protection Agency, Air and Energy Engineering Research Laboratory, Research
       Triangle Park, NC.  EPA 600/9-89-066.

Galbraith, S. T.J Brennan, T.; Osborne, M. C. (1988) Residential construction code impacts on radon.  In:
       Proceedings of the 1988 joint CSCE/ASCE national conference on environmental engineering, Vancouver.

Guo, A.; Tichenor, B. A. (1989) The temperature dependence of the release of perchlorethylene from dry cleaned
       fabrics.  Submitted to Environmental Research for publication.

Henscbd, D. B.  (1988) Radon reduction techniques for detached  houses, technical guidance, 2nd ed.  U.  S.
       Environmental Protection Agency, Air and Energy Engineering Research Laboratory,  Research Triangle
       Paik, NC.  EPA 625/5-87-019.

Hensche], D. B.j Scott, A. G. (1987) Testing of indoor  radon reduction techniques in eastern Pennsylvania:  an
       update.  In: Indoor radon II: Proceedings of 2nd APCA international specialty conference on indoor radon,
       April, Cherry Hill, NJ.

Hensche], D. B.; Scott, A. G. (1987) Some results from the demonstration of indoor radon reduction measures in
       block basement houses. In: Seifert, B.; Esdorn, H.; Fischer, M.; Rueden, H.; Wegner, J., eds., Indoor air
       '87: Proceedings of the 4th international conference on indoor air quality and climate, v. 2, environmental
       tobacco smoke, multicomponent studies, radon, sick buildings, odours and irritants, byperreactivities and
       allergies, August, Berlin, Federal Republic of Germany. Institute for Water, Soil and Air Hygiene; pp. 340-
       346.
    "        t                                                                                    *
Henschel, D. B.; Scott. A. G. (1986) The EPA program to demonstrate mitigation measures for  indoor radon:
       Initial results.  In: Indoor radon: Proceedings of an APCA international specialty conference, Philadelphia,
       PA; pp. 110-121.

Henschel. D. B.; Scott, A. G.; Findlay, W. 0.; Robertson, A. (1988) Testing of indoor radon reduction methods
       in 16 houses around dayton.  In:  Proceedings of the 1988 EPA-sponsored symposium on radon and radon
       reduction technology, Denver, CO.

Hubbard, L. M.; Bolker, B.; Sosolow, R. H.; Dickerhoff, D.; Mosley, R. B. (1988) Radon dynamics in a house
       heated alternately  by forced air and by electric resistance.  In:  Proceedings of the 1988 EPA sponsored
       symposium on radon and radon reduction technology, Denver, CO.

Hubbard L. M.; Sanchez, D. C.; Harrje, D. T.; Gadsby, K. J.; Turk, B. H. (1987) A review of selected state-
       of-the-art applications of diagnostic measurements for radon mitigation planning. In: Proceedings of the 198?
       ASCE national conference on environmental engineering, Orlando, FL; pp. 308-313.

Hubbard, L. M; Sanchez, D. C. et al. (1988) Radon entry into detached dwellings:  House dynamics and mitigation
       techniques. Radiation Protection Dosimetry, U24, N14, 513-518.

Hubbard, L. M. et al. (1989) Radon dynamics in a house heated alternatively by forced air and by electric
       resistance.  U. S. Environmental Protection Agency, Air and Energy Engineering Research Laboratory.
       Research Triangle Park, NC. EPA 600/9-89-006.

-------
Jackson, M. D.; Clayton, R. K.; Stephenson, E. E.; Guyton, W. T. (1988) EPA's indoor air quality test house:
       2. Kerosene heater studies. In:  Proceedings of the 1988 EPA/APCA symposium on measurement of toxic
       and related air pollutants.  EPA 600/9-88-015.

Jackson, M. D.; Clayton, R. K.; Stephenson, E. E.; Guyton,  W. T.; Bunco, J. E. (1987) EPA's indoor air
       quality test house, 1. Baseline studies. In:  Proceedings of the 1987 EPA/APCA symposium on measurement
       of toxic and related air pollutants. EPA 600/9-87-010.

Jackson, M. D.; Rasor, S. A.; Clayton, R. K.; Stephenson, E. E. (1988) Particulate and organic emissions from
       invented kerosene heaters, test house study. In: Proceedings of the apca international specialty conference
       on combustion processes and the quality of the indoor environment, in press.

Kaschak, W., M.; Gilroy, D. G.; Tracey, R. H.; Henschel, D. B. (1988) Assessment of the effectiveness of radon-
       resistant features in new house construction.  In:  Proceedings of the 1988 EPA sponsored symposium on
       radon and radon reduction technology, Denver, CO.

Kashdan, E. R.; Sickles, J. E.; Ranade, M. B. (1984) Review of recent research in indoor air quality.  Research
       Triangle Park, NC:  U.S. Environmental Protection Agency, Industrial Environmental Research Laboratory;
       EPA report no.  EPA 600/2-84-099.  Available from: NTIS, Springfield, VA; PB84-206515.

Leaderer, B. P.; Sabcgez, D. C. (1987) Characterization of indoor sources of air contaminants:  Report on technical
       conference.  U. S.  Environmental Protection Agency, Air and Energy Engineering Research Laboratory,
       Research Triangle Park, NC.  EPA 600/0-87-014.

Leovic, K. W.  (1988) Radon in schools. In:  Proceedings of indoor air quality conference,  Florida West Coast
       Chapter of ASHRAE and  Florida Power Corporation, Clearwater Beach, FL.

Leovic, K. W.  (1988) Radon in schools.  In:  Proceedings of the 1988 EPA sponsored symposium on radon and
      . radon reduction technology, Denver,CO.
Leovic, K. W.; Craig, A. B. (1989) Radon reduction techniques in schools - interim technical guidance.
       Report Between Office of Radiation Programs.  EPA 520/1-89-020.
Joint
Leovic, K. W.; Craig, A. B.; Sautii, D. W. (1988) Characteristics of schools with elevated radon levels.  In:
       Proceedings of the 1988 EPA sponsored symposium on radon and radon reduction technology, Denver,
       CO.

Leovic, K. W.; Craig, A. B.; Saurn, D. W. (1990) Radon mitigation in schools -part 1. American Society Heating,
       Refrigerating and Air-conditioning Engineers Journal (ASHRAE) 32(1):  40-45.

Leovic, K. W.; Sanchez, D. C.; Craig, A. B. (1988) Radon mitigation choices in the United States-A comparison
       of private and public sector developments.  Radiation Protection Dosimetry 24, N14:  513-518.

Leovic, K. W.; Sanchez, D. C.; Craig, A. B. (1988) Radon mitigation choices in the United States-A comparison
       of private and public sector developments. In: Proceedings of the 4th international symposium on the natural
       radiation environment, Lisbon, Portugal.

Mathews, T. C. et al. (1989) Impact of heating and air conditioning system operation and leakage on ventilation
       and intercompartinent transport: Studies in unoccupied and occupied tennessee valley homes.  Submitted
       to the Journal of the Air Pollution Control Assoc. of publication.

-------
Matbews, T. G. et al. (1989) Radon diagnostics: Subslab communication and permeability measurements.  U. S.
       Environmental Protection Agency, Air and Energy Engineering Research Laboratory, Research Triangle
       Park, NC.  EPA 600/9-89-006A.

Matthews,  T.  G.;  et  al.  (1987) Interlaboratory comparison of formaldehyde emissions  from particleboard
       underlayment in small-scale environmental chambers.  J. Air Pollut. Control Assoc. 37: 1320-1326.

Merrill, R. G.; Steiber, R. S.;  Martz, R. F.; Nehns, L. EL (1987) Screening methods for the identification of
       organic emissions from indoor air pollution sources. Atmos.  Environ. 21: 331-336.

Michaels, L. D.; et al. (1987) Development and demonstration of indoor radon redaction measures for 10 homes
       in clinton, new jersey. EPA 600/8-87-027.

Mosley, R. B.;  Henscbel, D. B. (1988) Application of radon reduction methods.  U. S. Environmental Protection
       Agency, Air and Energy Engineering Research Laboratory, Research Triangle Park, NC.  EPA 625/5-88-
       024.

Mumford, J. L.; He, X. Z.; Chapman, R. S.;  Cao, S. R.; Harris, D. B.; Li, X. M.; Xian, Y. L.; Jiang, W.
       Z.; Xu, C. W.; Chiang, J. C.; Wilson, W. E.; Cooke, M. (1987) Lung cancer and indoor air pollution
       in Xuan Wei, China. Science (Washington, DC) 235: 217-235.

Mumford, J. L.; Harris, D. B.; Bruce, D; Williams, K; Chuang, J. C.; Cooke, M. (1987) Indoor air sampling
       and mutagenicity studies of emissions from unvented coal combustion.  Environ. Sci. Technol. 21: 308-
       311.

Nehns, L. H.; Mason, M.  A.; Tichenor, B. A. (1986)  The effects of ventilation rates and product loading on
       organic emission rates from particleboard. In:  Proceedings'of the ASHRAE conference iaq '86: managing
       indoor air  for  health and energy conservation, April,  Atlanta,  GA.  American Society of Heating,
       Refrigerating and Air-Conditioning Engineers, Inc.; pp. 469-485.

Osborne, M. C. (1987) Four common diagnostic problems that inhibit radon mitigation.  J.  Air Pollut. Control
       Assoc. 37: 604-607.

Osborne, M. C. (1988) Radon-resistant residential new construction.  U. S. Environmental Protection Agency, Air
       and Energy Engineering Research Laboratory, Research Triangle Park, NC.  EPA 600/8-88-087.

Osborne, M. C. (1987) Resolving the radon problem in clinton, new jersey, houses.  In:  Seifert, B.; Esdorn, H.;
       Fischer, M.; Rueden, H.; Wegner, J., eds., Indoor air '87: Proceedings of the 4th international conference
       on indoor air quality and climate, v. 2, environmental tobacco smoke, multicomponent studies, radon, sick
       buildings, odours and irritants, hyperreactivities and allergies, August, Berlin, Federal Republic of Germany.
       Institute for Water, Soil and Air Hygiene; pp. 305-309.

Osborne, M. C.;  Brennan  T. (1987) Practical problems reducing radon in homes. In: Proceedings of the 1987
       ASCE national conference on environmental engineering, Orlando, FL; pp. 314-320.

Osborne, M. C.; Brennan, T. (1988) Radon—practical problems encountered during efforts to reduce concentration
       in houses.  The Journal of CIS, Batiment International Building Research and Practice 16(6):  363-366.

Osborne, M. C.; Brennan,  T.; Michaels, L. D. (1987) Radon mitigation in 10 clinton, new jersey bouses: A case
       history. In:  Proceedings of the 2nd international specialty conference on indoor radon, Cherry Hill, NJ.

-------
Osborne, M. C. et al. (1988) Radon reduction in an crawl space house. J. Environ. Engineering 115(3):
       589.
574-
Owen, M. K.; Ensor, D. S.; Boris, L. S.; Tucker, W. G. (1986) Effects of office building heating and ventilation
       system parameters on respirable particles. In:  Proceedings of the ASHRAE conference iaq' 86: managing
       indoor air for  health and energy conservation, April,  Atlanta, GA.  American Society  of Heating,
       Refrigerating and Air-Conditioning Engineers,  Inc.; pp. 510-522.

Owen, M. K.; Ensor, D. S.; Boris, L. S.; Tucker, W. G.; Sparks, W. E. (1988) Particle size distribution for an
       office aerosol. Submitted to Environmental Sci. and Tech.  for publication.

Perkins, R. L.; Starner, K. K.; Sparks, L. E. (1988) Asbestos in residential environments. In:  Proceedings of
       the 1988 EPA/APCA symposium on measurement of toxic and related air pollutants. EPA 600/9-88-015.
                                                                                                  i
Pugh,  T. D. (1989) Radon Resistant construction guidelines for use in florida.   U. S. Environmental Protection
       Agency, Air and Energy Engineering Research Laboratory, Research Triangle Park, NC.  EPA 600/X-89-
       XXX.

Ramanathan,  K.; Debler, V. L.; Kosusko, M.; Sparks, L. E. (1988) Evaluation of control strategies for volatile
       organic compounds in indoor air. Environ. Prog. 7(4): 230-235.

Pyle, B. E.; Osborne, M. C.; Brennan, T. (1988)  Radon mitigation in crawl space houses in nashville, tennessee.
       In:  Proceedings of the 81st annual APCA meeting, Paper No. 88-107.4.

Redford, D.; Jackson, M.; Gentile, J.; Oberacker, D.; Boehm, P.; Werme, C. (1988) Assessing potential effects
       of incinerating organic wastes at sea: using research to answer management questions.  Marine Poll. Bull.
       19: 599-601.

Redford, D.; Jackson, M.  Oberacker, D.; Cooke, M.; Degner, K.; Boehm, P.; Werme, C. (1988) Assessing
       potential effects of incinerating hazardous wastes at sea:   development and  field-testing of the marine
       biological assessment sampler.  In:  Proceedings of the 7th international ocean disposal symposium, in press.

Reist, P. C.; Reaves, J. C.; White, J. B. (1987) Developmental status of the indoor air source emissions database.
       In:  Seifert, B.; Esdoro, H.; Fischer, M.; Rueden, H.; Wegner, J., eds., Indoor air '87:  Proceedings of the
      ! 4th international conference on indoor air quality and climate, v.  1, volatile organic compounds, combustion
       gases, particles and fibres,  microbiological agents, August,  Berlin, Federal Republic of Germany. Institute
       for Water, Soil and Air Hygiene; pp. 63-68.

ReTzan, K. L. (1989) Radon reduction in  a crawl space house.  Journal of Environ. Engineering 115(3):  574-
       589.

Sanchez, D. C.  (1987) A review of the Canadian and Swedish experience for the control of indoor radon. In:
       Proceedings of international specialty conference on indoor radon, April, Cherry Hill, NJ; pp. 92-106.

Sanchez, D. C.  (1989) Technical  issues related to emission  releases from subslab radon mitgation systems. In:
       Proceedings of the 1989 national  conference on environmental engineering,  american society of civil
       engineers.

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Sanchez, D. £.; Dudney, C. S. (1988) A comparison of indoor radon concentrations determined by'passive carbon
       monitors and continuous radon monitors. In: Proceedings of the 1988 joint CSCE/ASCE national conference
       on environmental engineering, Vancouver, B.C. pp. 647-654

Sanchez, D. E.; Henschel, D. B. (1986) Radon reduction techniques for detached houses, technical guidance. U. S.
       Environmental Protection Agency, Air and Energy Engineering Research Laboratory, Research Triangle
       Park, NC.  EPA 625/5-86-019.

Sanchez, D. C.; Hubbard, L. M.; Harrje, D.; Turk, B. H. (1987) The use of diagnostic measurements to enhance
       die selection and effectiveness of radon mitigation for detached dwellings. In: Seifert, 8.; Esdom, H.;
       Herscher, M.; Rueden, H.; Wegner, J., eds., Indoor air '87: Proceedings of the 4th international conference
       on indoor air quality and climate, v. 2, environmental tobacco smoke, multicomponent studies, radon, sick
       buildings, odours and irritants, hyperreactivities and allergies, August, Berlin, Federal Republic of Germany.
       Institute for Water, Soil and Air Hygiene; pp. 370-375.

Sanchez, D. C.; Mason, M.; Norris, C. (1987) Methods and results of characterization of organic emissions from
       an indoor material. In: Symposium on the characterization of contaminant emissions from indoor sources;
       Chapel Hill, NC. Atmos. Environ. 21: 337-345.

Sawn, D. W.; Craig, A. B.; Leoric, K.  W. (1990) Radon mitigation in schools -part 2.  American Society of
       Heating, Refrigerating and Air-Conditioning Engineers (ASHRAE)

Saum, D. W.; Craig, A. B.; Leovic, K. W. (1988) Radon reduction systems in schools.  In:  Proceedings of the
       1988 EPA sponsored symposium on radon and radon reduction technology, Denver, Co.

Scott, A. G.; Robertson, A. (1988) Follow-up alpha-track monitoring in 40 eastern Pennsylvania houses with indoor
       radon reduction systems  (winter 1987-88).  U. S. Environmental  Protection  Agency, Air and Energy
       Engineering Research Laboratory, Research Triangle Park, NC.  EPA 600/8-88-098.

Scott, A. G; Robertson, A.; Flndlay, W. O. (1988) Installation and testing of indoor radon reduction techniques
       in 40 eastern Pennsylvania houses.  EPA-600/8-88-002.

Scott, A. G.; Sanchez, D.  C. (1988)  Assessment of diagnostic measurements for selection of residential radon
       mitigation.   In:  Proceedings  of the 1988 joint CSCE/ASCE  national conference  on environmental
       engineering. Vancouver, pp. 655-660.

Sextro, R. G.; Harrison, J.; Moed, B. A.; Revzan,  K. L.; Turk, B. H.; Grimsrud, D. T.; Nero, A. V.;
       Sanchez, D. C.; Tticbman, K. Y.  (1987) An intensive study of radon and remedial measures in New Jersey
       homes: preliminary results.  In: Seifert, B.; Esdorn, H.; Fischer, M.; Rueden,  H.; Wegner, J., eds.. Indoor
       air '87: proceedings of the 4th international conference on indoor air quality and climate, v. 2, environmental
       tobacco smoke, multicomponent studies, radon,  sick buildings, odours and irritants, hyperreactivities and
       allergies, August, Berlin, Federal Republic of Germany. Institute for Water, Soil and Air Hygiene; pp. 295-
       299.                                            x

Sickles, J. E.; et al. (1987) A summary of indoor-air quality research through 1984.  EPA report no. EPA 600/9-
       87-020.

Sparks, L. E.; Jackson, M. D.; Tichenor, B. A. (1988) Comparison of EPA test  house data with prediction of an
       indoor air quality model.  In:   Engineering solutions to indoor air problems,  proceedings of the ashrae
       conference iaq '88.

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Simla, L. E.; Tucker, W. G.; Horis, L. S.; Owne, M. K.; Ensor, D. S. (1990) Particle size distributions for
       an office aerosol.  Accepted for publication by Aerosol Sci. Tech.

Sparks, L. E.; Viner, A. S.; Ramanathan, K.; Hanley, J. T.; Smith, D. D.; Ensor, D. S. (1990) Air cleaners
       for indoor air pollution control. Abstract submitted to ACS for publication.

Tichenor, B. A. (1988) Air pollutants from surface materials:  Factors influening emissions and predictive models.
       Accepted for publication by Environ. International.

Tichenor, B. A.  (1990)  Measurement of organic compound emissions using small chambers.   Accepted for
       publication by Environ.  International.

Ticheoor, B. A. (1987) Organic emission measurements via small chamber testing. In: Seifert, B.; Esdom, H.;
       Fischer, M.; Rueden, H.; Wegner, J., eds., Indoor air '87: proceedings^the 4th international conference
       on indoor air quality and climate, v.  1, volatile organic compounds, combustion gases, particles and fibres,
       microbiological agents,  August, Berlin, Federal Republic  of Germany. Institute for Water, Soil and Air
       Hygiene; pp.  8-15.

Tichenor, B. A.; Guo, Z, (1988) The effect of ventilation on emission rates of wood finishing materials. Submitted
       for publication to Environ. International.

Tichenor, B. A.; Jackson, M. D.; Merrill, R. G. (1986) Measurement of organic emissions from indoor materials -
       small chamber studies. In: Proceedings ofthe EPA/APCA symposium on measurement of toxic air pollutants,
       April, Raleigh, NC. EPA 600/9-86-013.

Tichenor, B. A.; Mason, "M. A. (1987) Evaluation of organic emissions to the indoor environment via small chamber
       testing.  In:  Proceedings of the  1987 EPA/APCA symposium on measurement of toxic and related air
       Pollutants, May, Research Triangle Park, NC.  EPA 600/19-87-010.

Tichenor, B. A.; Mason, M. A. (1988)  Organic emissions from consumer products to the indoor environment.
       JAPCA38(3): 264-268.

Tichenor, B. A.; Sparks, L. E.; Jackson, M. D.; Guo, Z.; Mason, M. A.  (1989) Emissions of perchloroethylene
       from dry cleaned fabrics.  Accepted  for publication by Atmospheric Environ.

Tichenor, B. A.; Sparks, L. E.; White, J. B.; Jackson, M. D. (1989) Evaluating sources of indoor air pollution.
       Submitted to JAPCA. for publication.

Tucker, W. G. (1986) Research overview:  sources of indoor air pollutants.  In:  Proceedings of the ASHRAE
       conference IAQ '86: managing indoor air for health and energy conservation; Atlanta, GA: American Society
       of Heating, Refrigerating and Air-Conditioning Engineers, Inc.; pp. 395-404.

Tucker, W. G. (1987) Chairman's summary, session I. Characterization of emissions from combustion sources:
       controlled studies.  In:  Symposium on the characterization of contaminant emissions from indoor sources;
       Chapel Hill, NC. Atmos. Environ. 21: 281-284.

Tucker, W. G. (1988) Emissions of air pollutants from indoor materials: An emerging design consideration.  In:
       Proceedings of the 5th f*p*M*Q building and construction congress.

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Turk, B. H.; Harrison, J.; Prill, R. J. Sextro, R. G. (1988) Preliminary diagnostic procedures for radon control.
       U. S. Environmental Protection Agency, Air and Energy Engineering Research, Research Triangle Park, NC.
       EPA 600/8-88-084.

U. S. Environmental Protection Agency (1986) Radon reduction techniques for detached houses: technical guidance.
       Washington, DC:  Office of  Research and Development.  EPA 625/5-86-019.

U. S. Environmental Protection Agency (1986) Radon reduction methods: a homeowner's guide. EPA report no.
       OPA-86-005.

U. S. Environmental Protection Agency (1987) Characterization of indoor sources of air contaminants:  report on
       a technical conference. EPA 600/9-87-014.

U. S. Environmental  Protection Agency (1987) Radon reduction methods: A homeowner's guide, Second edition.
       EPA report no. OPA-87-010.

U. S. Environmental Protection Agency (1988) Radon reduction techniques for detached houses, technical guidance,
       Second edition.  EPA report no. EPA 625/5-87-019.

U. S. Environmental Protection Agency (1987) Removal of radon from household water. EPA report no. OPA-
       087-011.

Viner, A. S.; Ramanathan, K.J Hanley, J. T.; Smith, D. D.; Ensor, D. S.;  Sparks, L. E. (1989) Air cleaners
       for indoor air pollution control.  In:  Proceedings of the EPA/APCA symposium.

Werme, C.; Boehm, P.; Cooke, M.; Oberacker, D.; Jackson, M.; Redford, D. (1988) Assessing potential effects
       of incinerating organic, wastes at sea:  Development and field testing of the marine incineration biological
       assessment sampler.  Marine Pollut. Bull. 19:  602-604.

White, J. B.; Leaderer, B. P.; Boone, P. M.; Hammond, S. K. (1987)  Characterization of particle and organic
       emissions from unvented kerosene space heaters.  In: Seifert, B.; Esdom, H.; Fischer, M.; Rueden, H.;
       Wegner, J., eds. Indoor air '87: proceedings of the 4th international conference on indoor air quality and
       climate, v.  1,  volatile organic compounds, combustion gases, particles  and fibres,  microbiological agents,
       August, Berlin, Federal Republic of Germany.  Institute for Water, Soil and Air Hygiene; pp. 84-88.

White, J. B.; Leaderer,  B.  P.; Boone, P. M.; Hammond, S.  K.;  Mumford, J.  L. (1987) Chamber studies
       characterizing organic emissions from kerosene space heater,  hi:  Proceedings of the 1987 EPA/APCA
       symposium on measurement of toxic and related air pollutants.  EPA 600/9-87-010.

White, J. B.; Reaves, J. C.; Reist, P. C.; Mann, L. S. (1988) A data base on the sources of indoor air pollution
       emissions,  hi: Proceedings of the ASHRAE conference iaq '88.

Williamson, A. D.; Martin, R. S.; Harris, D.  B.; Ward., T. E. (1987)   Design and characterization of an
       isokinetic sampling train for particle  size measurements using emission  gas recycle. APCA 37:  249.

Witter, K.; Craig, A. B.; Saum, D. (1988) New-construction techniques and hvac over-pressurization for radon
       reduction in schools,  hi: Proceedings of the ASHRAE conference iaq '88, Atlanta, GA. pp. 69-76.

Yamamoto, T.; Owen, M. K.; Ensor, D. S.; Sparks, L. E.  (1989) Design and verification of a computer
       simulation for office aerosol.  To be submitted to Environ. Sci. and Tech.

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PRESENTATIONS AND OTHER REPORTS
Barber, J. ML; ffinterlong (1989) Computer modeling of subslab ventilation systems in florida. Presented at the
       Health Physics Society's 34th Annual Meeting Albuquerque, NM.

Brennan T.;  Osborne, M. C.  (1987) Monitoring before and after radon mitigation.  Presented at the ASTM
       Symposium on Design and Protocol for Monitoring Indoor Air Quality; April.

Brennan, T.; Osborne, M. C.  (1988) Overview of radon-resistant new construction.  Presented at the 1988
       Symposium on Radon and Radon Reduction Technology, Denver, CO.                    .

Clayton, R. K.; Stephenson, E. E.; Jackson, M. D. (1988) EPA's indoor air quality test house moth cake studies.
       Presented at the  1988 EPAMPCA Symposium on Measurement of Toxic and Related Air Pollutants, May,
       Raleigh, NC.                        ,                                              •
                                          1                                              it
Collective IAB Work (1986)  Radon reduction methods:  A homeowner's guide.  U. S.  Environmental Protection
       Agency, Air and Energy Engineering Research Laboratory, Research Triangle Park, NC.  OPA-86-005.

Craig, A. B. (1988) An overview of EPA's radon mitigation program. Presented at the American Lung Association,
       Orlando, FL.

Craig, A. B. (1988) Description of EPA's radon mitigation program.  Presented at the Florida Coordinating Council.

Craig, A. B.  (1987) Description of EPA's radon mitigation program.  Presented at the State Radiation Workshop,
       Atlanta, GA.

Craig, A. B.  (1988) Diagnosis and solutions of indoor radon problems.  Presented at the CRCPD, Nashville, TN.

Craig, A. B. (1987) Discussion of EPA's experience in  radon mitigation.  Presented  at the State Radiation
       Workshop,  Atlanta, GA.

Craig, A. B. (1988) Discussion of EPA's experience in radon mitigation. Presented at the NC Health Physics
       Society, Wilmington, NC.

Craig, A. B. (1988) EPA's Experience in mitigating indoor radon problems. Presented at the South Dakota Energy
       Workshop,  Sioux Falls, SD.

Craig, A. B.  (1988) EPA's radon mitigation program. Presented at the National Radon Association, Atlanta,  GA.

Craig, A. B.  (1987)  Presentation of EPA's  radon mitigation demonstration program.  Presented at the AMA
       Workshop, Hartford, CT.

Craig, A. B.  (1988) Presentation of EPA's radon research program. Presented at the American Lung Association,
       Minneapolis, MN.

Craig, A. B.  (198$) Radon diagnosis and abatement in residential dwellings. Presented at the Radiological Health
       Conference, October, New Castle,  DE.

Craig, A. B.  (1986) Radon diagnosis and abatement in residential dwellings. Presented at the Region I Workshop,
       New Hampshire.

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Craig, A. B. (1986) Radon diagnosis aad abatement in residential dwellings. Presented at the Region IV Workshop,
       Atlanta, GA.

Craig, A. B. (1986) Radon diagnosis and abatement in residential dwellings. Presented at the Region V, VI, and VH
       Workshops, Kansas City.

Craig, A. B. (1986) Radon diagnosis and abatement in residential dwellings. Presented at the Region VI Workshop,
       Tulsa, OK.

Craig, A. B. (1988) Radon mitigation techniques.  Presented at the Iowa HBA, Des Moines, Iowa.

Craig, A. B. (1988) Results of EPA's radon mitigation program.  Presented at the National Radon Association,
       Atlanta, GA.

Craig, A. B. (1987) Status of EPA's radon mitigation demonstration program. Presented at the 19th Annual National
       Conference on Radiation Control, May, Boise, Idaho.

Craig, A. B. (1987) Status of EPA's radon mitigation demonstration program. Presented at the SMIBIA Workshop,
       MD.

Craig, A. B. (1987) Overview of EPA's radon mitigation program.  Presented at the NYU Workshop, New York,
       NY.

Craig, A. B. (1987) Overview of EPA's radon mitigation program. Presented at the Iowa State Workshop, Des
       Moines, Iowa.

Craig, A. B.; darns, D. B.; Leovic, K. W.; Pyle, B. (1990) Radon diagnostics and mitigation in public schools
       in nashville, tn.  To be presented at the 1990 Internationa] Symposium on Radon and Radon Reduction
       Technology, Atlanta, GA.

Cnim, J. M. (1986) Indoor air pollution source database. Presented at the 79th Annual Meeting of the Air Pollution
       Control Association, June, Minneapolis, MN and the Pittsburgh, PA Air Pollution Control Association; paper
       no. 86-52.6.

Davidson, D. I. (1986) Pollutant emission factors  for gas stoves: a  literature survey. CR-812543-01-0.

Dorsey, J.; Steiber, R.; Martz, R. (1989) Proposed procedure for the detection and identification of cfc's and hcf s
       in foams.

Dorsey, J.; Steiber, R.; Jackson, M. (1990) Comparison of iab in-house analytical systems: phase 1  bag sample.
       IAB Report 90-3.

Dudney, C. S. et al. (1989) Indoor radon in tennessee valley  houses: Summer/winter comparisons.  Presented at
       the Health Physics Society's 34th Annual Meeting, Albuquerque, MM.

Dunn, J. E. (1986) Isolation of wall effects in chamber tests of indoor building materials. Presented to the National
       Institute of Environmental  Medicine, Karolinska Institute and  Department of Psychology, December,
       Stockholm University.
                                                  10

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Dam, 1. E. (1986) Madding sources and sinks for indoor air emissions. Presented to the Institute of Hygiene,
       December, Aarhus University, Denmark.

Dunn, J. E.; Tichenor, B. A. (1987) Compensating for wall effects in iaq chamber tests by mathematical modeling.
       Presented at the 80th Annual Meeting of the Air Pollution Control Association, June, New York, NY and
       me Pittsburgh, PA Air Pollution Control Association; paper no. 87-83.4.

Ensor, D. S. et al. (1989) Indoor air quality simulator for personal computers.  Presented at the APCA Annual
       Meeting, San Diego, CA.

Ensor, D. S.;  Viner, A. S.; Hanley, J. T.; Lawless, P. A.; Ramanathan, K.; Owen, M. K.; Yamamoto, T.;
       Sparks, L, E. (1988) Air cleaner technologies for indoor air  pollution.  Presented at the American
       Association for Aerosol Research (AAAR), Chapel  Hill, NC.  .
                \                                               (>;
EPA Report (1989) Tar effluents from roofing of p-wing.  IAB Report 89-3.

Fowler, C. S.  et al. (1988) Subslab depressurizan'on demonstration in polk county,  florida slab-on-grade houses.
       Presented at the 1988 Radon Symposium, Denver, CO.

Guo, Z. S.; Rasor, S. A.; Sparks, L.; Tichenor, B.; Jackson, M. (1989) Study of indoor air movement by using
       carbon monoxide as a tracer.

Guo, Z.; Tichenor, B. A.; Dunn, J. E. (1990) On representing reversible sinks in IAQ models.  Abstract submitted
       for presentation at Indoor Air '90 Conferences, Toronto, Canada.

Harris, D.  B.  (1988) Radon measunnent methods used to  design and  evaluate residential  mitigation systems.
       Presented at the American Chemical Society Meeting, Atlanta, GA.

Harrje, D. T.; Hubbard, L. M.; Sanchez, D.  C. (1988) Diagnostic approaches to better solutions  of radon IAQ
       problems.  Presented at the CIS-Conference on Healthly Buildings, Stockholm.

Henschel, D. B. (1986) An overview of indoor radon mitigation alternatives and a summary of recent EPA mitigation
       test results.  Presented at the National workshop on radon gas—practical responses, May, Washington, DC.
       National Institute of Building Sciences.

Henschel, D. B.; Craig, A. B. (1986) An overview of indoor radon mitigation alternatives and a summary of recent
       EPA mitigation test results.  Presented at the National Convention of the American Institute  of Architects,
       June, San Antonio, TX.

Henschel, D. B.; Scott, A. G. (1986) The EPA program to demonstrate mitigation measures for indoor radon: initial
       results. Presented at the International Specialty Conference on Indoor Radon, February, Philadelphia, PA.
       Pittsburgh, PA: Air Pollution Control Association;  pp. 110-121.

Henschel, D. B. et al. (1989) A review of indoor radon reduction methods and of radon entry routes. Presented at
       the Public Radon Meeting Sponsored by the Orange County, NC Agricultural Extension Service.

Hubbard, L. M.; Sanchez, D. C.; et al. (1987) Radon entry into detached dwellings: house dynamics and mitigation
       techniques. Presented at the 4th International Symposium on the Natural Radiation Environment, December,
       Lisbon, Portugal.
                                                   11

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Hubbard, L. M,; Sanchez, D. C.; et al. (1987) Radon: controlling the source. Presented at the 1987 Annual
       Meeting of the American Institute of Chemical Engineers, November, New York, N.Y.

Jackson, M. D. (1988) IAQ test bouse mothcake testing July 1987. IAB Report 88-5.

Jackson, M. D. (1988) IAQ test house studies 1987. IAB Report 88-3.

Jackson, M. D.; Clayton, R. K.; Stepbenson, E. E.; Guyton, W. T. (1988) EPA's indoor air quality test house
       kerosene heater studies.  Presented at the 1988 EPA/APCA Symposium on Measurement of Toxic and
       Related Air Pollutants, May, Raleigh, NC.

Jackson, M. D.; Guo, Z.; Rasor, S.j Krebs, K. (1989) Study of indoor air movement by using carbon monoxide
       as a tracer.  IAB Report 89-4.

Jackson, M. D.; Sparks, L. E.; Ticbenor, B. A.; Guo. Z.; Krebs, K. A.; Rasor, S. (1990) Air and pollutant
       movement in building(s) can be evaluated using CO as a surrogate. Abstract submitted for Presentation at
       the Indoor Air '90 Conference, Toronto, Canada.

Jackson, M. D.; Steiber, R. (1990) Samples analyzed by gas chromatography/mass spectometry fy89.  LAB Report
       90-1.

Leovic, K. W. (1989) EPA's program in indoor air quality.  Presented for Kevin Teichman at the Florida West
       Coast Chapter ASHRAE Conference, Tampa.

Leovic, K. W. (1989) Radon in residential, education, and commercial buildings. Presented to the Triangle Chapter
       ASHRAE.

Leovic, K. W. (1990) Radon protocol in schools. To be presented at the Georgia Tech Research Institute's Annual
       Indoor Air Quality Symposium and Workshop, Atlanta, GA.

Leovic, K. W. (1989) Radon reduction methods:  A homeowner's guide (third edition).  U.  S. Environmental
       Protection Agency, Air and Energy Engineering Research Laboratory, Research Triangle Park, NC.

Leovic, K. W.; Craig, A. B.; Saum, D. (1990) Radon mitigation experience in difficult-to-mitigate schools.  To
       be presented at the 1990 International Symposium on Radon and Radon Reduction Technology, Atlanta,
       GA.

Leovic, K. W.; Craig, A. B.; Saum, D. (1989) The influences of hvac design and operation on radon mitigation
       of existing school buildings.  Presented at the ASHRAE, IAQ '89, San Diego, CA.
Maschandreas, D.; White, J. (1989) Fugitive emissions of
       study.  IAB Report 89-6.
                                                            from vented appliances in residences:  A pilot
Murane, D.; Craig, A. B. (1987) Interim guide to radon reduction in construction.  U. S. Environmental Protection
       Agency, Air and Energy Engineering Research Laboratory,  Research Triangle Park, NC. OPA-87-009.

Neims, L. H.; Mason, M. A.; Ticbenor, B. A. (1987) Determination of emission rates and concentration levels of
       p-dichlorobenzene.  Presented at the 80th Annual Meeting of the Air Pollution Control Association, June,
       New York, NY.  Pittsburgh, PA: Air Pollution Control Association; paper no. 87.
                                                  12

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Osborne, ML C. (1987) Radon reduction methods:   A homeowner' guide (2nd edition). U. S. Environmental
       Protection Agency, Air and Energy Engineering Research Laboratory, Research Triangle Park, NC.  OPA-
       87-010.

Osborae, M. C. (1987) Resolving die radon problem in clinton, nj houses.  Presented at the 4th International
       Conference on Indoor Air Quality and Climate, Berlin.

Osborne, M. C.; Brennan T. (1987) Practical problems of reducing radon in houses.  Presented at the 1987 National
       Conference on Environmental Engineering, July, Orlando, FL.
                                    \
Osborne, M. C.; Brennan, T.; Michaels, L. D. (1987) Radon mitigation in 10 clinton, new jersey houses: case
       history. Presented at the 2nd International Specialty Conference on Indoor Radon, April, Cherry Hill, NJ.
                                    i1'
Osborne, M. C.; Brennan, T.; Michaels, L. D. (1987) Monitoring radon reduction in clinton, new jersey houses.
       Presented at (he 80th Annual Meeting of the Air Pollution Control Association, June, New York, NY.
       Pittsburgh,  PA: Air Pollution Control Association; paper no. 87-83.7.

Radsby, D.  T.; Hubbard, L. M.; Harrje, D. T.; Sanchez, D. C. (1988) Rapid Diagnostics:  Subslab and wail
       depressurization systems for control of indoor radon.  Presented at the 1988 Radon Symposium, Denver,
       CO.

Rasor, S. A.; Guo, Z.; Jackson, M. (1989) Mothcake test no. 3. IAB Report 89-5.

Samfield, M. (1987) Air infiltration into structures: a literature review and analysis.  AEERL Internal Report IAB
       87-1; July.

Samfield, M. (1989) Ambient air quality  data base for organic compounds. IAB Report 89-8.

Samfield, M. (1985)  Indoor air paniculate matter: a literature survey.  Research  Triangle Park,  NC:  U. S.
       Environmental Protection Agency; HATB report 85-1 [unpublished]; p. 3.

Samfield, M. (1988) Indoor air pollution. Presented at a Meeting of the Tri-County Heating, Ventilating and Air
       Conditioning Engineers, Durham, NC.

Samfield, M. (1988) Indoor air quality data base for organic compounds.  IAB Report 88-2.

Samfield, M. (1990) Indoor air quality data base for organic compounds.  IAB Report 88-3.

Samfield, M. (1986) Radon infiltration into structures and mitigation techniques - a literature review.  Research
       Triangle Park, NC: U. S. Environmental Protection Agency; HATB report 86-3 rev. [unpublished].

Samfield, M. (1987) Residential air-to-air heat exchanger:  a literature review and analysts. LAB Report 87-3.

Samfield; M. (1989) Theory of indoor pollutant emission rates from sources: A literature survey. IAB Report 89-
       1.

Sanchez, D. C.; Dudney, C. S. (1988) A comparison of indoor radon concentrations determined by passive carbon
       monitors and continuous radon monitors.  Presented at the 1988 Joint CSCE/ASCE National Conference on
       Environmental Engineering, Vancouver.
                                                  13

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Sanchez. D. C. et al. (1989) Occupational and environmental exposures to radon: A perspective for mitigators.
       Presented at the 1989 National Conference on Environmental Engineering, Austin.

Sum, D.j Sanchez, D. C. (198$ Radon mitigation performance in three houses. Presented at the 1988 Symposium
       on Radon and Radon Reduction Technology, Denver, CO.

Sparks, L. (1988) IAB model version 1.0. IAB Report 88-1.

Sparks, L. (1989) Preliminary evaluation of air cleaners for indoor air quality, IAB Report 89-7,

Sparks, L. £.; Jackson, M. D.; Tichenor, B. A. (1988) Comparison of EPA test house data with predictions of
       an indoor air quality model. Presented at the IAQ '88, April, Atlanta, GA. American Society of Heating,
       Refrigerating  and Air Conditioning Engineers, Inc.

Sparks, L. £.; Jackson, M. D; Tichenor, B. A.; White, J. B. (1989) The EPA  indoor air quality model-
       verification experiments and sample uses. Presented at the IAQ'89, ASHRAE, San Diego.

Sparks, L. £.; Tichenor, B. A.; Jackson, M. D.; White, J.; Dorsey, J. A.; Steiber, R. S. (1990) An integrated
       approach to studying the impact of sources and sinks on indoor air quality.  Abstract submitted for
       presentation at the Indoor Air '90 Conference, Toronto, Canada.

Sparks, L. E.$ Tucker. W. G. (1990) An indoor air quality model for estimating individual exposure to indoor
       pollutants.  Abstract submitted for presentation at the Indoor Air  '90 Conference, Toronto, Canada.

Tichenor, B. A.; Guo, Z.; Dunn, J. £.; Mason, M. A. (1990) Evaluation of indoor air pollutant sinks for vapor
       phase organic compounds. Abstract submitted for presentation at  the Indoor Air '90 Conference, Toronto,
       PanaHa             •                                                                       .
                                                                                                   *
Tichenor, B.  A.;  Molhave, L.; Dunn, J. £.  (1990) International comparison of chamber test methods for
       determining organic compounds.  Abstract  submitted for presentation at the Indoor Air '90 Conference,
       Toronto, Canada.

Tichenor, B. A.; Mason, M. A. (1986) Characterization of organic emissions from selected materials in indoor use.
       Presented at the 79th Annual Meeting of the Air Pollution  Control Association, June, Minneapolis, MN.
       Pittsburgh, PA: Air Pollution Control Association; paper no. 86-16.S.

Tichenor, B. (1990) Evaluating organic emissions for building materials and products. IAB Report 90-2.

Tichenor, B. A.;  Mason, M. A. (1987) Organic emissions from consumer products to the indoor environment.
       Presented at the 80th Annual Meeting of the Air Pollution Control Association,  June, New  York,  NY.
       Pittsburgh, PA: Air Pollution Control Association; paper no. 87-81.8.

Tucker, W. G. (1989) Control of residential indoor air contaminants. Presented at the Healthy Buildings Conference
       sponsored by Northeast Utilities and United Illuminating.

Tucker, W. G. (1987) Engineering research program in indoor air quality: radon reduction and development.

Tucker, W. G. (1989) EPA activities is indoor air quality. Presented to the National Association of Home Builders,
       Atlanta, GA.
                                                  14

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Tucker, W. G. (1986) EPA's engineering research program in indoor air quality:  Source characterization and IAQ
       control.

Tucker, W. G. (1989) EPA's indoor air engineering r St d program: Sources and control of iaq problems.  Presented
       to the Chemical Specialties Manufacturers Association, Washington, DC.

Tucker, W. G. (19849 EPA research on indoor air quality.  Presented at the 79th Annual Meeting of the Air
       Pollution Control Association, June, Minnneapolis, MN. Pittsburgh, PA: Air Pollution Control Association;
       paper no. 86-11.5.
         (
          *
Tucker, W. G.  (1990) Low-emitting materials and products:  Where do we  stand?  Abstract submitted for
       presentation at Indoor Air '90 Conference, Toronto, Canada.
         d
Tucker, W. G.  (1987) Source characterization of indoor air pollution. Presented at the  Indoor Air Quality
       Symposium, Georgia Tech Research Institute, September, Atlanta, GA.

Tucker, W. G. (1988) Source characterization  and iaq control (mitigation).  Presented at the State Indoor Air
       Research Needs Meeting, National Governor's Association, Washington, DC.

Tucker, W. G. (1987) Symposium chairman's  summary on sources of indoor vapor-phase organic compounds.
       Presented at the 4th International Conference on Indoor Air Quality and Climate, Berlin.

Turk, B. H.; Harrison, J.; Prill, R. J.; Sextro; R. G. (1987) Interim report on diagnostic procedures for radon
       control. Washington, DC: Office of Research and Development;  report no. LBL-23089.

Turner, W.; Leovic, K. W.; Craig, A. B. (1990) The effects of hvac design and operation on radon  entry into
       school  buildings.  To be presented at the 1990 International Symposium on Radon and Radon Reduction
       Technology, Atlanta, GA.

U. S. Environmental Protection Agency (1986) EPA's engineering research program in indoor air quality: source
       characterization and iaq control.  Air and Energy Engineering Research Laboratory; draft AEERL internal
       report.

U. S. Environmental Protection Agency (1987) Engineering research program in indoor air quality:  radon reduction
       research and development.  EPA/AEERL internal report, March.

U. S. Environmental Protection Agency (1987)  Interim guide to radon reduction in new construction. EPA report
       no. OPA-87-009; August.

White, J. B. (1988)  IAB/NC dept. of health services cooperative sick buildings investigations:  Optimist park
       swimming pool. IAB Report 88-4.

White, J. B.; Leaderer, B. P. (1987) Chamber studies characterizing organic emissions from kerosene space heaters.
       Presented at the 1987 EPA/APCA Symposium on Measurement of Toxic and Related Air Pollutants, May,
       Research Triangle Park, NC.

White, J. B.$ Leaderer, B. P. (1988) Chamber studies characterizing organic emissions from kerosene space heaters,
       phase n.   Presented at the 1988 EPA/APCA Symposium  on Measurement of Toxic and Related Air
       Pollutants,  May, Raleigh, NC.
                                                  15

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Wigger, K.; Bullers, T.; Zoske, P.; Lewie, K. W.; Saum, D. W.  (1990) Hectret ion chambers for radon
       measurements in schools during occupied and unoccupied periods. To be presented at the 1990 International
       Symposium on Radon and Radon Reduction Technology, Atlanta, GA.

Witter, K. A. (1987) Collection of field data for radon reduction research. EPA/AEERL Internal Report LAB 87-
       2.

Witter, K. A.; Sanchez, D. C.; Craig, A. B. (1987) Radon mitigation choices in the United States - a comparison
       of private and public sector developments.  Presented at the 4th International Symposium on the Natural
       Radiation Environment, December, Lisbon, Portugal.

Witter, K. A.; Craig, A. B.; Saum, D. (1988) New-construction techniques and hvac over pressurization for radon
       reduction in schools.   Presented at the ASHRAE Indoor  Air Quality Conference, April,  Atlanta, GA.
       American Society of Heating, Refrigerating and Air Conditioning Engineers, Inc.
                                                  16

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          PUBLICATIONS AND PRESENTATIONS FROM THE
                         ENVIRONMENTAL CRITERIA
       AND ASSESSMENT OFFICE'S INDOOR AIR PROGRAM
PUBLICATIONS
        , H. M.; Berry, M. A.; Childs, N. £.; Mage, D. T. (1986) Health effects associated with indoor air
      pollutants. In: Proceedings of the ASHRAE conference iaq '86: managing indoor air for health and energy
      conservation, April, Atlanta, GA. American Society of  Heating, Refrigerating and Air Conditioning
      Engineers, Inc.; pp. 53-70.

Ammann, H. M. (1987) Effects of indoor pollutants on sensitive populations. Gin. Ecol. 5: 15-21.

Ammann, H. M. (1989) Potential health effects from kerosene heater emissions.  In:  Proceedings of the 1988
      APCA specialty conference on emissions for combustion processes, Niagara Falls,  NY.

Anunaim, H. M.; Barry, M. A. (1987) Health risk profile for indoor air. In: Seifert, B.; Esdom, H.; Fischer, M.;
      Rueden, H.; Wegner, J., eds., Indoor air '87:  proceedings of the 4th international conference on indoor
      air quality and Climate, v. 2, environmental tobacco smoke, multicomponent studies, radon, sick buildings,
      odours and irritants, hyperreactivities and allergies; August; Berlin, Federal  Republic of Germany. Institute
      for Water, Soil and Air Hygiene; pp.  227-231.

Berry, Michael A. (1989) Assessing the health consequences and risks of toxic pollutants in indoor environments.
      In:  Proceedings of the air toxics symposium, air and waste management association, Raleigh, NC.

Berry, Michael A. (1989)  Indoor air quality:   Assessing health impacts and risks.  In:   Proceedings of the
      international symposium industrialization and emerging environmental issues. University of Occupational
      and Environmental Health, Kitakyushu, Japan.

Berry, Michael A. (1988)   A national indoor air program: Opportunity for research and cooperation.   In:
      Proceedings of the APCA '88, air pollution control association meeting, Dallas, TX.

Berry, Michael A. (1989)  Strategic per II controllo degli inquinanti indoor.  City Council of Milan, Italy.

Gold, Karen W.; Berry, Michael  A.;  Naugle, Dennis F. (1989) Indoor  concentrations of environmental
      carcinogens.  World Health Organization, in press.

Peterson, Max R.; Berry, Michael A.; Naugle, Dennis F. (1989)  Methods  of analysis for environmental
      carcinogens.  World Health Organization, in press.

U. S. Environmental Protection Agency (1989) A review of indoor air quality risk characterization studies. Office
      of Health and Environmental Assessment, Environmental Criteria and Assessment Office, Research Triangle
      Park, NC.
                                              17

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U. S. Environmental Protection Agency (1989) Development of a risk characterization framework.  Office of Health
       and Environmental Assessment, Environmental Criteria and Assessment Office, Research Triangle Park, NC.

U. S.  Environmental Protection Agency  (1989)  Indoor air  reference bibliography.   Office of Health and
       Environmental Assessment, Environmental Criteria and Assessment Office, Research Triangle Park, NC.
       EPA 600/8-89/067F.

U. S. Environmental Protection Agency (1989) Methods of analysis for environmental carcinogens.  Office of
       Health and Environmental  Assessment, Environmental Criteria and Assessment Office, Research Triangle
       Park, NC.

U. S. Environmental Protection Agency (1989) Overview of indoor concentrations of environmental carcinogens.
       Office of Health and Environmental Assessment, Environmental Criteria and Assessment Office, Research
       Triangle Park, NC.

U. S. Environmental Protection Agency (1989) Use of benzene measurement data in risk characterization estimates:
       A preliminary approach.  Office of Health  and Environmental  Assessment, Environmental Criteria and
       Assessment Office, Research Triangle Park, NC.
                                                 18

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PRESENTATIONS AND OTHER REPORTS
         , H. (1989) Biological contaminants of the indoor environment.  Presented at the University of North
       Carolina School of Public Health, Center for Environmental Research, Occupational Safety and Health.

Ammann, H. M. (1986) Health implications of indoor air pollutants. Presented to Than Distributors.

Ammann( H. M. (1986) Woodsmoke health effects. Presented to Northwest Air Pollution Control Association;
       September, Seattle, WA.

Ammann, Q,  j£ (1987) Effects of air pollution on sensitive populations. Presented at the 5th  International
       Symposium on Man and His Environment in Health and Disease, February, Dallas, TX.

Ammann, H. M. (1987) Health implications of indoor pollutants. Presented to Conference on Air Cleaners, October,
       Raleigh, NC.

Ammann, H. M. (1987) Indoor air pollution and health effects. Presented to the Southeastern Association of Health
       Professionals, July, Annapolis, IN.

Ammann, H. M. (1988) Panel participant, Region 8 integrated air toxics meeting. Recommendations for local indoor
       air policy to municipal officials and representatives of health departments.

Berry, Michael A. (1989) Environmental issues and opportunities for the professional cleaner. South Professional
       Cleaners Association, January, Gastonia, NC.

Berry, Michael A. (1989) Health effects of indoor air pollutants.  The University of North Carolina School of
       Public Health Alumni Conference, February, Chapel Hill, NC.

Berry, Michael A. (1990) The impact of indoor air quality on health and welfare. Georgia Institute of Technology,
       Annual Indoor Air Quality Symposium, February, Atlanta, GA.

Berry, Michael A. (1987) Indoor air and carpet.  International Institute of Carpet and Upholstery. Care, May,
       Seattle, WA.

Berry, Michael A.  (1990)   Indoor air health effects.  Georgia Institute of Technology, Annual Indoor Air
       Symposium,  February, Atlanta, GA.

Berry, Michael A. (1988) Indoor air issues. Carpet and Rug Institute, Annual Technical Meeting, October, Panama
       City, FL.

Berry, Michael A. (1987) Indoor air pollution.  Florida Power and Light, Environmental Conference, October,
       Orange Springs, FL.

Berry, Michael A. (1989)  Indoor air research. Chemical Specialties Manufacturing Association, April, Chicago,
       IL.

Berry, Michael A. (1989)  Indoor air research. Consumer Federation of America, June, Washington, DC.
                                                  19

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Berry, Michael A. (1988) Indoor environments and public health.  The Bureau of National Affairs, Sick-Building
       Conference, November, Baltimore, MD.

Berry, Michael A. (1988)  Overview of indoor air pollutant risks.  Society for Risk Analysis, October, Research
       Triangle Park, NC.

Berry, Michael A. (1989) Position paper and statement on asbestos. American Society of Heating, Refrigerating
       and Air-Conditioning Engineers (contributing author) ASHRAE Health Committee, ASHRAE.

Kotchmar, D. J.; Comfort, B. M.; Elias, R. W.; Garner, J. H. B.; Tilton, B. £.; Grant, L. D. (1990) Critical
       health issues associated with review of the scientific criteria for oxides of nitrogen.  To be Presented at 83rd
       Annual Meeting of the Air and Waste Management Association, Pittsburgh, PA.

 North Atlantic Treaty Organization Committee on the Challengers of Modern Society (1989) The Implications
       of Indoor Air Quality for Modern Society. (M. A. Berry, editor and contributing author). CCMS Report
       No. 183.  Based on a meeting held in Erice, Italy.

Raub, J. A.; Grant, L. D. (1989) Critical health issues associated with review of the scientific criteria for carbon
       monoxide.  Presented at the 82nd Annual Meeting of APCA, Anaheim, CA.

World Health Organization (1989) Indoor air quality:  Organic pollutants (contributing author), EURO Reports
       and Studies 111, Regional Office for Europe, Copenhagen.
                                                  20

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                  PUBLICATIONS AND PRESENTATIONS  FROM
           THE ENVIRONMENTAL MONITORING SYSTEMS
                 LABORATORY'S INDOOR AIR PROGRAM
PUBLICATIONS
Axley, J. (1988) Progress toward a general analytical method for predicting indoor air pollution in buildings: phase
      m report. U. S. Department of Commerce, National Bureau of Standards.

Axley, J.; Grot, R. (1986) General indoor air pollution concentration model:  phase n report. U. S. Department
      of Commerce, National Bureau of Standards.

Childers, J. W.; Wilson, N. K.; Barbour, R. K. (1989) Analysis of environmental air sample extracts by gas
      chromatography/matrix isolation-infrared spectrometry.  In: Proceedings of the 7th international conference
      on fourier transform spectroscopy, E.  G. Cameron, ed., SPEI - The International Society for Optical
      Engineering,  BeUingham, WA: Vol 1145, pp. 611-612.

Childers, J. W.; Wilson, N. K.; Barbour, R.  K. (1989) Analysis of woodsmoke-impacted air sample extracts by
      gas chromatography/matrix isolation-fourier transform infrared spectrometry. In: Proceedings of the 1989
      international  symposium on measurement of toxic and  related air pollutants, A&WMA, Pittsburgh, PA,
      VTP-13.   .                                                 .               .

Childers, J. W.; Wilson, N. K.; Barbour, R. K. (1990) Gas chromatograhy/matrix isolation-fourier  transform
      infrared spectrometry for the determination of polynuclear hydrocarbons hi environmental air sample extracts.
      In: Proceedings of the 12th international symposium on polynuclear aromatic hydrocarbons, W. E. May and
      M. J. Cooke, eds.,  in preparation.

Childers, J. W.; Wilson, N. K.; Barbour, R. K. (1989) Gas chromatography/matrix isolation-infrared spectrometry
      for the identification of polycyclic aromatic hydrocarbons in urban air particulate matter.  Appl. Spectrosc.
      43(8):  1344-1349.

Chuang, J. C.; Holdren, M. W.; Kuhlman, M. R.; Wilson, N. K. (1989) Methodology of indoor air monitoring
      for polynuclear aromatic hydrocarbons and related compounds.  Proceedings of the  1989 international
      symposium on measurement of toxic and related air pollutants, A&WMA, Pittsburgh, PA: Pub.  VTP-13.

Chuang, J. C.; Holdren, M. W.; Wilson, N. K. (1990) The presence of dichloromethane on cleaned XAD-2 resin:
      A potential problem and solutions.  Environ. Sci. Technol., in press.

Chuang, J.  C.; Kuhlman, M.  R.; Wilson, N. K. (1990) Evaluation  of a method for sampling and analysis  of
      nicotine and polynuclear aromatic hydrocarbon in indoor air. Environ. Sci. Technol., in press.

Chuang, J.  C.; Mack, G. A.; Koetz, J. R.; Petersen, B. A. (1985) Pilot study of sampling and analysis for
      polynuclear aromatic compounds in indoor air. Research Triangle Park, NC: U. S. Environmental Protection
      Agency, Environmental Monitoring Systems Laboratory; EPA report no. EPA/600/4-86/036.
                                              21

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Chuang, J. C.; Mack, G. A.; Kuhhnan, M, R.; Wilson, N. K. (1990) Polycyclic aromatic hydrocarbons in indoor
       mi outdoor air la an eight-home pilot study. Atmos. Environ., submitted for publication.

Chuang, J. C.; Wilson, N. K. (1986) Preparation of air samples for bioassay. Research Triangle Park, NC: U. S.
       Environmental Protection Agency, Environmental Monitoring Systems Laboratory.

Chuang, J. C.; Mack, G. A.; Peterson, B. A.;  Wilson, N. K.  (1986) Identification and quantification of nitro
       polynuclear aromatic hydrocarbons in ambient and indoor air particulate samples. In: Cooke, M.; Dennis,
       A. J., eds., Polynuclear aromatic hydrocarbons: chemistry, characterization, and carcinogenesis. Columbus,
       OH; BatteUe Press; pp. 155-171.

Chuang, J. C.{ gohlman, M.  R.; Wannan, S. W.; Bridges,  C. (1987) Evaluation of sampling and analysis
       methodology for  nicotine and polynuclear aromatic hydrocarbons in indoor air. Research Triangle Park,
       NC: U. S. Environmental Protection Agency, Environmental Monitoring Systems Laboratory; EPA report
       no. EPA 600/4-87/031.

Chuang, J. C.; Mack, G. A.; Mondron, P. J.; Petersen, B. A. (1984) Development of sampling and analytical
       methodology for polynuclear aromatic compounds in air. Research Triangle Park, NC: U. S. Environmental
       Protection Agency, Environmental Monitoring Systems Laboratory; EPA report no. EPA 600/4-85/065.

Flndley, M. W.; Stetter, J. R. (1988) Construction and testing of electrochemical NO personal exposure monitor.
       Transducer Research Inc., contract no. 68-02-4406, in press.

Highsmith, V. R.; Rodes, C. E.; Hardy, R. J. (1988) Indoor particle concentrations associated with using tap water
       in  portable humidifiers. Environ. Sci. and Technol.:  1109-1112.

Howes, J. £.;  Merriman, T. L.; Ortiz, C. A.; McFarland, A.  R.; Kuhlman, M. R. (1986) Development of a
       sampler for particulate-associated and low volatility organic pollutants in residential air. Research Triangle
       Park, NC: U. S.  Environmental Protection Agency, Environmental Monitoring Systems Laboratory; EPA
       report no. EPA 600/4085/079.

Kosczynski, S. L. (1989) Multidimensional gas chromatographic  determination of cotinine as a marker compound
       for particulate-phase environmental tobacco smoke. J. Chromatogr, 463: 253-260.

Kosczynski, S. L. (1987) Multidimensional gas chromatographic  determination of cotinine as a marker compound
       for paniculate phase environmental tobacco smoke. Atmos. Environ.

Lewis, R.  G. (1988) Standard practice for sampling and analysis of pesticides and polychlorinated biphenyls in indoor
       atmospheres, hi:  Annual  book of standards,  v. 11.03; Pittsburgh,  PA, in press.

Lewis, R. G. (1988) Determination of pesticides and polychlorinated biphenyls in indoor air. hi: Environmental
       carcinogens: methods of analysis and exposure measurement, v. 12, Indoor air; Geneva, Switzerland; World
       Health  Organization, in press.

Mack, G. A.;  Stockrahm, J. W.; Chuang, J. C. (1989) Statistical comparison of results of two indoor air pilot
       studies. U. S. Environmental Protection  Agency, Research Triangle Park, NC; AREAL-RTP-101; EPA
       600/3-89/055.

Mitra, S.; Wilson,  N. K. (1990)   Polynuclear aromatic hydrocarbons in indoor air:  Data interpretation using
       principal component analysis.  Atmos. Environ., submitted for publication.
                                                  22

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Mulik, J. D.; Lewis, R. G. (1988) Recent developments in passive sampling devices.   In:  Advances in Air
       Sampling, Lewis Publishers, pp. 117-131.

Mulik, J. D.; Lewis, R. G.; McClenny, W. A.; Williams, D. D. (1989) Modification of a high efficiency passive
       sampler to determine nitrogen dioxide or formaldehyde in air. Anal. Chem.:  187-189.

Malik, J. D.; Williams, D. E. (1987) Passive sampling devices for NO. In: Proceedings of the 1986 EPA/APCA
       symposium on measurement of toxic air pollutants, pp. 61-70 and proceedings  of the 1987 EPA/APCA
       symposium on measurement of toxic air pollutants, pp. 387-397.

Ozkaynak, EL; Ryan, P.; Allen, G.; Turner, W. (1982) Indoor air quality modeling: compartmental approach with
       reactive chemistry. Environ. Int. 8:

Pellizzari, E. D.; Sheldon, L. S.; Sparacino, C. M.; Bursey, J. T.; Wallace, L.; Bromberg, S. (1984) Volatile
       organic levels in indoor air. In: Berglund, B.; Lindvall,  T.; Sundell, J., eds.j Indoor air:  Proceedings of
       the 3rd international conference on indoor air quality and climate, v.4, chemical'characterization and personal
      ' exposure; August; Stockholm, Sweden. Stockholm, Sweden: Swedish Council for Building Research; pp. 303-
       308. Available from: NTIS, Springfield, VA; PB85-104214.

Pleil, J. D.; Oliver, K. D. (1987) Measurement of concentration variability of volatile organic compounds in indoor
       air: automated operation of a sequential syringe sampler  and subsequent gc/ms analysis. TN-4420-87-01.

Pleil, J. D.; Oliver, K. D.; McClenny, W. A. (1987) Time-resolved measurement of indoor exposure to volatile
       organic compounds. In: Seifert,  B.; Esdorn, H.; Fischer,  M.; Rueden, H.; Wegner, J., eds.,  Indoor air
       '87: Proceedings of the 4th international conference.on indoor'air quality and climate, v. 1, volatile organic
       compounds, combustion gases, particles and fibres, microbiological agents; August; Berlin, Federal Republic
       of Germany. Institute for Water, Soil and Air Hygiene; pp. 164-169.

Roberts, J. W.;  Ruby, M. G.  (1989) Development of a high volume sampler for pesticides in floor dust.  U. S.
       Environmental Protection Agency, Research Triangle Park, NC; EPA 600/4-88/036.

Schaaff, A. (1987) Analysis of semi volatile compounds in passive air samples by on-line supercritical fluid extraction
       gas chromatography. Research Triangle Park, NC: U. S.  Environmental Protection Agency, Environmental
       Monitoring Systems Laboratory; EPA report no. EPA 600/X-87/372.

Shelton, L.; Zelon, H.; Sickles, J.; Eaton, C.; Hartwell, T. (1988) Indoor air quality in six buildings.  RTI
       contract no. 68-02-4068.

Shelton, L.; Sparacino, C.; Gutknecht, W.; Laird, L.; Warner, M. (1984) Monitor in and around public access
       buildings, part II: analytical protocols. EPA contract 68-02-4068.

Shelton, L.; Hardy, R.; Hartwell, T.; Whitmore, R.; Zelon, H.;  Pellizzari, E.  (1987) Total assessment
       methodology  special study-indoor air study. RTI.

Tosteson, T. D.; Ware, J. H. (1987) Designing a logistic regression study using surrogate measures for exposure
       and outcome. TR no. 23; September.

U. S. Environmental Protection Agency (1989) Indoor air quality and work environment study: EPA headquarters*
       building volume I - employee survey, 19K-1003. U. S. Environmental Protection Agency, Washington,  DC
       19K-1003.
                                                  23

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U. S. Environmental Protection Agency (1990) Indoor air quality and work environment study: EPA headquarters'
       buildings volumes n - results of environmental monitoring study: U. S. Environmental Protection Agency,
       Atmospheric Research and exposure Assessment Laboratory, Research Triangle Park, NC (final version
       expected to be available April 1990).

Vo-Dinh,  T.; Miller, 6. H.; Abbott, D. W.; Reitz, K.  R. (1986)  Evaluation of screening  methodology for
       polynuclear aromatic pollutants in air in residential environments. Research Triangle Park,  NC: U. S.
       Environmental Protection Agency, Environmental Monitoring Systems Laboratory.

Wilson, N. K.; Childers, J. W.; Harbour, R. K. (1990) Application of matrix isolation infrared spectroscopy to
       analysis for polynuclear aromatic hydrocarbons in environmental samples. In: W. E. May and M. J. Cooke,
       eds., Proceedings of the 12th International Symposium on Polynuclear Aromatic Hydrocarbons, Gordon and
       Breach,  New York, in press.

Wilson, N. K.;  Chuang, J. C.; Kuhlman, M. R.; Mack, G. A. (1990) Sampling semivolatile organic compounds
       in indoor air.  In:  Proceedings of the 5th international conference on indoor air quality and climate, in
       preparation.

Wilson, N. K.; Chuang, J. C.; Kuhlman, M. R.; Mack, G. A. (1990) Measurements of PAH and their derivatives
       in indoor air. In: W. E. May and M. J. Cooke, eds., Proceedings of the 12th international symposium on
       polynuclear aromatic hydrocarbons, in  preparation.

Wilson, N. K.; Chuang, J.  C.;  Kuhlman, M.  R.; Mack, G. A.  (1990) Measurement of polycyclic aromatic
       hydrocarbons and other semivolatile organic compounds in indoor air. In: Proceedings of the EPA/A&WM A
       international symposium of total exposure assessment methodology, in press.

Wilson, N. K.; Kuhlman,  M. R.; Chuang, J. C.; Mack, G. A.;  Howes, J. E.,'Jr.  (1989) A quiet sampler for
       the collection of semivolatile organic pollutants in indoor air. Environ. Sci. Technol. 23(9):  1112-1116.

Wilson, N. K.;  Petersen, B. A. (1984) Evaluation of sampling and analysis methodology  for polynuclear aromatic
       compounds in indoor air.  Research Triangle Park, NC: U. S. Environmental Protection Agency,
       Environmental Monitoring Systems Laboratory; EPA report no. EPA 600/M-84-008.

Wilson, N. K. (1985) An evaluation of a room-temperature  phosphorescence-based personal exposure  monitor for
       polynuclear aromatic hydrocarbons in residential air. Research Triangle Park, NC: U. S.  Environmental
       Protection Agency,  Environmental Monitoring Systems Laboratory.

Wilson, N. K.;  Chuang, J. C. (1988) Indoor air levels of pah and related compounds in an eight-home pilot study.
       In: W. E. May and M. Cooke, eds., Proceedings of the 12th international symposium on  polynuclear
       aromatic hydrocarbons; September 1987; Gaithersburg, MD. New York, NY; Marcel Dekker, in press.
       EPA 600/D-88/000.
                                                  24

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 PRESENTATIONS AND OTHER REPORTS
Barbour, R. K.; Childers, J. W.; Wilson, N. K. (1988) Identification of semivolatile organic compounds in selected
       air sample extracts by gas chromatography/matrix-isolation infrared spectrometry. Presented at the Cryolect
       Users' Workshop; May; Research Triangle Park, NC.

Childers, J. W.; Wilson, N. K.; Barbour, R. K. (1989) Analysis of environmental air sample extracts by gc/mi-
       ir spectrometry. Presented at the 1989 International Conference on Fourier Transform Spectroscopy, Fairfax,
       VA.

Childers, J. W.; Wilson,  N. K.;  Barbour,  R. K.  (1989)  Analysis of  woodsmoke-impacted air by gas
       chromatography/matrix isolation-fourier transform infrared spectrometry.  Presented at the 1989 Cryolect
       Users' Meeting and Symposium on GC/MI-ER, Chicago, IL.
                                                i
Childers, J. W.; Wilson, N. K.; Barbour, R. K.  (1989) Gas chromatography/matrix isolation-fourier transform
       infrared spectrometry for the determination of polynuclear aromatic hydrocarbons in environmental air
       sample extracts.  Presented  at the 12th International Symposium on Polynuclear Aromatic Hydrocarbons,
       Gaithersburg, MD.

Childers, J. W.; Wilson, N. K.; Barbour, R. K. (1990) Identification of organic chemicals in mutagenic fractions
       of air sample extracts.  To be presented at the Symposium on Matrix  Isolation Spectroscopy, 1990 FACSS
       meeting, Cleveland, OH.

Childers, J. W.; Wilson, N- K.; Barbour, R. K.  (1989) Identification of semivolatile organic compounds in air
       sample extracts by gas chromatography/matrix isolation-fourier transform infrared spectrometry.  Presented
       at the 103rd NC Sectional Conference, North Carolina Section, American Chemical Society; Chapel Hill,
       NC.

Childers, J. W.; Wilson, N. K.;  Barbour  (1989)  Analysis of environmental  air sample extracts by  gc/mi-ir
       spectrometry.  Presented at the 1989 International Conference on Fourier Transform Spectroscopy, Fairfax,
       VA.

Chuang, J. C.; Holdren, M. W.;  Kuhlman,  M. R.; Wilson, N.  (1989) Methodology of indoor air monitoring
       for  polynuclear aromatic hydrocarbons and related compounds.   Presented at the 1989 EPA/A&WMA
       International Symposium on Measurement of Toxic and Related Air Pollutants, Raleigh, NC.

Chuang, J. C.; Mack, G.  A.; Kuhlman,  M.  R.; Wilson,  N. K. (1990)  Polycyclic  aromatic compound
       concentrations in residential air associated with cigarette smoking and gas or electric heating and cooking.
       To be Presented at the 1990  EPA/A&WMA International Symposium on Measurement of Toxic and Related
       Air Pollutants, Raleigh, NC.

Chuang, J. C.; Mack, G. A.; Petersen, B. A.; Wilson, N. K (1984) Identification and quantification of nitro
       polynuclear aromatic hydrocarbons in ambient and indoor air particulate samples. Presented at the 9th Inter-
       National Symposium on Polynuclear Aromatic Hydrocarbons; October; Columbus, OH. Abstract no. 85.

Grot, R.; Axley, J. (1987) The development of models for the prediction of  indoor air quality in  buildings.
       Presented at the 8th Annual ATVC Conference; Berlin, Federal Republic of Germany.
                                                 25

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Hasabdnaby, N. A.; Ware, J. H.; fUUcr,  W. A.  (1988) Indoor air pollution and pulmonary performances:
       Investigating errors in exposure assessment TR no. 28; May.

Kopczynski, S.  L. (1988) Multidimensional gas chromatognphic determination of cotinine as a marker compound
       for particulate-phase environmental tobacco smoke.  Presented at the Eastern Analytical Symposium, New
       York.

Lewis, R. G. (1987) Sampling organic and inorganic gases and vapors in occupied homes. Presented at toe ASHRAE
       Annual Meeting; June; Nashville, TN.

Lewis, R. G.; Mulik, J. D. (1987) Development and evaluation of instruments for monitoring indoor air quality
       and personal respiratory exposure. Presented at the American Industrial Conference; May; Montreal, Canada.

Lewis, R. G.; Wallace, L. (1987) Instrumentation and methods for measurement of indoor air quality and related
       factors.  Presented at the ASTM Symposium on Design and Protocol for Monitoring Indoor Air quality;
       April; Cincinnati, OH.

Mulik, J. D. (1988) Determination of nitrogen dioxide exposures in occupied homes.  Presented at the SERMAC
       Meeting, Atlanta, GA.

Mulik, J. D. (1990) Passive sampling devices.  Training course at Harvard School of Public Health.

Mulik, J. D.  (1990) Passive sampling devices for monitoring human exposure.  Training Course Presented at the
       TEAM Conference, Las Vegas,  NV.

Mulik, J. D. (1988) Passive sampling devices for NO2, formaldehyde, and selected volatile organics. Presented at
       the Georgia Tech Air Quality Symposium, Atlanta, CA.

Mulik, J. D.; Lewis, R. G. (1987) Recent developments in passive sampling  devices.  Presented at the American
       Conference of Governmental Industrial Hygienists Symposium:   Advances in Air  Sampling; February;
       Asilomar, CA.

PleU, J. D.; McClenny, W. A.; Oliver, K. D. (1988) VOC  exposure from indoor use of household products.
       Presented at the Pittsburgh Conference and Exposition;  paper no. 320; February; New Orleans, LA.

Pleil, J.  D.; McClenny, W. A.; Oliver, K.  D.  (1988) Peak exposures and dissipation rate measurements of
       halogenated volatile organic compounds in indoor air. Presented at the American Society for Mass
       Spectroscopy Conference; paper no. 784; June; San Francisco, CA.

Vo-Dinh, T.; Miller, G. H.; Wilson, N. K.  (1986) Screening polynuclear aromatic pollutants in ambient air by
       synchronous luminescence.  Presented at the EPA/APCA Symposium on Measurement  of Toxic Air
       Pollutants; April; Raleigh, NC.

Whiton, R. S.; Cbilders, J. W. (1989) Identification of volatile and senrivolatile organic compounds associated
       with new carpet. Presented at the 1989 International  Conference on Fourier Transform  Spectroscopy,
       Gaithersburg, MD.

Whiton, R. S.; Childers, J. W. (1989) Identification of volatile and semivolatile organic compounds associated
       with new carpet. Presented at the 1989 EPA/A&WMA  International Symposium on Measurement of Toxic
       and Related Air pollutants, Raleigh, NC.
                                                  26

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Wilson, N. K; Chuang, J. C.; Kuhhnan, M. R. (1990) Sampling semivolatile organic compounds in indoor air.
       To be Presented at the 5th International Conference on Indoor Air Quality m& Climate, Toronto, Ontario,
Wilson, N. K.; Chuang, J. C; KnMman, ML R.; Mack, G. A. (1989) Measurement of PAH and their derivatives
       in indoor air.  Presented at the 12th International Symposium on Polynuclear Aromatic Hydrocarbons,
       Gaithersburg, MD.

Wilson, N. K.; Chuang, J. C.; KuMman, ML R.; Mack, G. A. (1989) Measurement of polycyclic aromatic
       hydrocarbons and other semivolatile organic compounds in indoor air.  Presented at the  EPA/A&WMA
       International Symposium on Total Exposure Assessment Methodology:  A New Horizan, Las Vegas, NV.

Wilson, N. K.; Lewis, R. G.; Chuang, C.  C.; Petersen, B. A.; Mack, G. A. (1985) Analytical and sampling
       methodology for characterization of polynuclear aromatic compounds in indoor air.  Presented at the 78tb
       Annual Meeting of the Air Pollution Control Association; June; Detroit, MI. Pittsburgh, PA: Air Pollution
       Control Association; paper no. 85-30A.2.

Wilson, N. K.; Vo-Dinb, T.; Chuang, J. C.; Lewtas, J. (1985) A comparison of passive with active sampling and
       analysis for polynuclear aromatic compounds in an indoor air pilot study.  Presented at the 10th International
       Symposium on Polynuclear Aromatic Hydrocarbons; October; Columbus, OH.
                                                 27

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   PUBLICATIONS AND PRESENTATIONS FROM THE HEALTH
 EFFECTS RESEARCH LABORATORY'S INDOOR AIR PROGRAM


 PUBLICATIONS
Andon, B.; Claxton, L.; Mumford, J. (1990) Analysis of mntageos by the nricrosuspension forward mutation assay
      in Salmonella typhimurium. IARC, Indoor Air; vol. 12.

Becker, S.; Jordan, S. L.; Orlando, G. S.; Korea, H. S. (1989) Ozone exposure down regulate human mitogen
      induced lymphocyte stimulation and proliferation. J. Environ. Tox. 26: 469-483.

Benignus, V. A.; Muller, K.; Barton, C.; Prah, J. (1987) Effects of low level carbon monoxide on compensatory
      tracking and event monitoring. Neurobehav. Toxicol. Teratol. 9: 227-234.

Benignus, V. A. (1986) Effect of breathing air containing contaminants such as CC^i CO and hydrocarbons at 1 and
      5 atmospheres. In: Hyperbarics and mixtures, no. 19, National Research Council.

Benignus, V. A. (1988) Effects of breathing  ordinary air at 1 and 5  atmospheres pressure:  CNS effects.  In:
      Hyperbarics and mixtures, National Research Council.

Benignus, V. A. (1987) Neurobehavioral effects of environmental tobacco smoke. In: Hyperbarics and mixtures,
      National Research Council.

Caka, F. M.; Eato'ugh, D. J.; Lewis, E. A.; Tang, EL; Hammond,  S. K.; Leaderer, B. P.; Koutrakis,  P.;
      Spengler, J. D.; Pasaro, A.; McCarthy, J.; Ogden, M. W.; Lewtas, J. (1989)  A comparison study of
      sampling techniques for nicotine in environments. In: Proceedings of the 1989 EPA/A&WMA International
      Symposium on Measurement of Toxic and Related Air Pollutants, Raleigh, NC, pp. 525-541.

Carson, J. L.; Collier, A. M.; Hu, S.; Smith, C. A. (1988) Pathologic changes in human ciliated nasal epithelium
      associated with acute low level exposure to sulfur dioxide. Environ. Res., in press.

Carson, J. L.; Collier, A. M.; Hu, S.; Smith, C. A.; Stewart, P. (1987) The appearance of compound cilia in the
      nasal mucosal of normal human subjects following acute in vivo exposure to sulfur dioxide. Environ. Res.
      42: 155-165.

Chapman, R. S.; Mumford, J. L.; Harris, D. B.; He, X. Z.; Jiang, W.; Yang, R. O. (1988) The epidemiology
      of lung cancer in Xuan Wei, China:  Current progress, issues, and research strategies. Arch. Environ. Health
      43(2): 180-185.

Claxton, L. D.; Morin, R. S.; Hughes,  T. J.; Lewtas, J. (1989) A genotoxic assessment of environmental tobacco
      smoke using bacterial bioassays.  Mutation Research 222:  81-99, U. S. Environmental Protection Agency,
      Health Effects Research Laboratory, Research Triangle Park, NC. EPA 600/J-89/014.
                                             28

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Coultas, D. B.; Samet, J. M.; Peake, G. T.; McCarthy, J.; Spengler, J.  (1987) Reliability and validity of
       questionnaire assessment of involuntary tobacco smoke exposure.  In: Seifert, B.; Esdom, H.; Fischer, M.;
       Rueden, H.; Wegner, J., eds. Indoor air '87: Proceedings of the 4th international conference on indoor air
       quality and climate, v. 2, environmental tobacco smoke, multicomponent studies, radon,  sick buildings,
       odours and irritants, hyperreactivities and allergies; August; Berlin, Federal Republic of Germany. Institute
       for Water, Soil and Air Hygiene; pp. 121-126.

DeMarini, D. M.; Kado, N. Y.; Lewtas, J. (1990) Analysis of mutagens by the microsuspension mutagenicity assay
       in Salmonella typhimurium.  IARC, Indoor Air; vol.  12.

Dockery, D. W.; Spengier, J. D.; Speizer, F. E.; Paris, B. G.; Ware, J. H.; Brunekreef, B. (1987) Associations
       of health status with indicators of indoor air pollution from an epidemiologic study in six U.S. cities. In:
       Seifert, B.; Esdom, H.; Fischer, M.; Rueden, H.; Wegner, J., eds. Indoor Air '87:  Proceedings of the
       4th international conference on indoor air quality  and climate, v. 2, environmental tobacco smoke,
       multicomponent studies, radon, sick buildings, odours and irritants, hyperreactivities and allergies; August;
       Berlin, Federal Republic of Germany. Institute for Water, Soil and Air Hygiene; pp. 203-208.

Eatough, D. J.; Caka, F. M.; Lewis, E. A.; Belnap, D.; Crawford, J.; Hansen, L. D.; Lewtas, J. (1990) An
       automated sampling system for the collection of enviromental tobacco  smoke constituents  in commercial
       aircraft.  In:  Proceedings of the 1989  EPA/A&WMA international symposium on measurement of toxic
       and related air pollutants, Raleigh, NC., pp. 565-576.

Folinsbee, L. J. (1989) Controlled human exposures to acid aerosols.  In:  U. S. Environmental Protection Agency
       Acid Aerosol Issue Paper, Environmental Criteria and Assessment Office, Office of Health and Environmental
       Assessment, Research Triangle Park, NC. EPA 600/8-88/005F.

Folinsbee, L. J. (1988) Human clinical inhalation exposure:  Exposure design,  methodology, and physiological
       responses. In: Gardner, D. E.; Crapo, J. D.; Massaro, E. J., eds.  Toxicology of the lung, pp.  175-199.

Folinsbee, L. J. (1989) Human health effects of airborne acid.  Environ.  Health Perspect. 79:  195-199.

Folinsbee, L. J.; Hazucha, M. (1989) Persistence of ozone-induced changes in lung function and airway reactivity.
       Proceedings of third  U.S.-Dutch international symposium:  atmospheric ozone research  and its  policy
       implications, pp. 483-492.

Folinsbee, L. J.; Schiesinger, R. B. (1989) Aerosol deposition and acid neutralization. In: U. S. Environmental
       Protection Agency, Acid Aerosols Issue Paper, Environmental Criteria and Assessment, Office of Health and
       Environmental Assessment,  Research Triangle Park, NC. EPA 600/8-88/005F.

Gerrity, T. W. (1988) Nasopharyngeal removal of inhaled ozone in humans and animals. In: Proceedings from
       the symposium on extrapolation modeling of inhaled particles and gases:  Lung dosimetry. Duke University
       Medical Center, Durham, NC, in press.

Gerrity, T. W.; McDonnell, W. F. (1989) Do functional changes in humans correlate with the airway removal
       efficiency of ozone? In: Proceedings of the third U.S.-Dutch international symposium: Atmospheric ozone
       research and its policy implications.

Gerrity, T. W.; McDonnell, W. F.; O'Neil, J. J. (1989) Experimental ozone dosimetry in humans.  J. Aerosol
       Sci.:  129-139.
                                                   29

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Goldstein, I. F.j Andrews, L. &; Lieber, K.; Foutrakis, G.; Kazembe, F.; Huang, P.; Hayes, C. (1987) Acute
       exposure to nitrogen dioxide and pulmonary function. In:  Seifert, B.; Esdom, H.; Fischer, M.; Rueden,
       H.; Wegner, J., eds. Indoor air '87:  Proceedings of the 4th international conference on indoor air quality
       and climate, v. 1, volatile organic compounds, combustion gases,  particles and fibres,  microbiological
       agents, August, Berlin, Federal Republic of Germany. Institute for Water, Soil and Air Hygiene; pp. 293-
       298.

Goldstein, G. M.; Collier, A.; Etzel, R.; Lewtas, J.; Haley, N. (1987) Elimination of urinary cotinine in children
       exposed to known levels of side-stream cigarette smoke. In:  Seifert, B.; Esdom, H.; Fischer, M.; Rueden,
       H.; Wegner, J., eds., Indoor air '87:  Proceedings of the 4th, international conference on indoor air quality
       and climate, v. 2, environmental tobacco smoke, multicomponent studies, radon, sick buildings, odours, and
       irritants, hyperreactivities and allergies, August, Berlin, Federal Republic of Germany.  Institute for Water,
       Soil and Air Hygiene; pp. 61-68.

Graham, D.; Henderson, F.; House, D. (1988) Neutrophil influx measured in nasal lavages of humans exposed to
       ozone.   Arch. Environ. Health 43(3):  228-233.

Hammond, S. K.; Mumford, J. L.; Henderson, F. W.; Lewtas, J. (1989) Exposure to enviromental tobacco smoke
       in the home. In:  Proceedings of the 1989 EPA/A&WMA international symposium on measurement of toxic
       and related air pollutants, May, Raleigh, NC.

Harbin, T. J.; Benignus, V. A.; Muller, 0. E.; Barton,  C. (1988) The effect  of low-level carbon monoxide
       exposure upon cortical evoked potentials in young and elderly men. Neurotoxicol. and Teratol. 10: 93-
       100.

Hatch, G. E.; Korea, H. S.; Aissa, M. (1989) A model for composition of animal and human alveolar dose and
       toxic effects of inhaled ozone.  Health Phys.  57(1):  37-40.

Henderson, F.  W.; Back, K. C.;  Benignus, V.; Bove, A. A.; Bradley,  M.;  Hong, S. K.; Horvath, S. M.;
       Jenkins, L. J.; Kobrick, J. L.; Leith, D. E.; Bennett, P.; Topulos, G. P. (1988) Submarine air quality,
       monitoring the air in submarines, health effects in  divers of breathing submarine air under hyperbaric
       conditions. National Research Council Report.  National Academy Press.

Henderson, F. W.; Graham, D. M.; Orlando, G. S.; Milholland, V. S.;  Harder, S. D.; Dubovi, E. J.; Seal,
       E. (1988) The immune response to rhinovirus infection in human volunteers exposed to ozone.  Am. Rev.
       Respir.  Dis. 137(5):  1124-1127.

Henderson, F. W.; Reid, H. F.; Morris, R.; Wang, 0. L.; Hu, P. C.; Helms, R.  W.; Forehand, L.; Mumford,
       J.; Lewtas, J.; Haley, N. J. (1989) Home air nicotine levels and urine cotmine-creatinine ratios in preschool
       children. American Review of Respiratory Disease 140:  197-201.

Horstznan, D. H. (1989) Sulfur-dioxide-induced bronchoconstriction in asthmatics exposed for short duration under
       controlled conditions: A selected review.  In:  Utell, M. J. and Frank, R., eds., susceptibility to inhaled
       pollutants, American Society for Testing and Materials, Philadelphia, PA.

Horstman, D.  H.;  McDonnell, W. F.; Abdul-Salaam, S; Folinsbee, L. J.;  Ives, P. J. (1989)  Changes in
       pulmonary function and airway reactivity due to prolonged exposure to near ambient ozone levels.  In:
       Schneider, T.  et al., eds., Proceedings of the third U.S.-Dutch international symposium:  Atmospheric
       research and its policy implications.
                                                  30

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Horstman, D. H.; McDonneU, W. F.; Abdul-Salaam, S.; Folinsbee, L. J.; Ives, P. J. (1989) Current USEPA
       research concerning more prolonged exposures of humans to low ozone concentrations. In: Brasser, L. J.;
       Mulder, W. C., eds., Man and his ecosystem, Proceedings of the eighth world clean air congress, 1:  1-
       6.

Jahnke, G. D.; Thompson, C. L.; Walker, M. P.; Gallagher, J. E.; Lucier, G. W.; DiAugustine, R. P. (1989)
       Multiple dna adducts in lymphocytes of smokers and nonsmokers determined by 32P-postlabeIing analysis.
       Cancer Research.

Kehri, H. D.; Horstman, D.; O'NeO, J.; Vincent, L.; Kowalsky, R.;  McCartney,  W.; Bromberg, P. (1989)
       Ozone induced changes in respiratory epithelial permeability. In:  Schneider, T. et al.,  eds., proceedings
       of the mud U.S.-Dutch international symposium:  Atmospheric  ozone research and its policy implications.

Koren, H. S. (1989) The potential use of immunological markers in determining susceptible individuals to inhaled
       pollutants.  In:  Utell, M. J.; Frank, R., eds., Susceptibility to inhaled pollutants, American Society for
       Testing and Materials, Philadelphia, PA.

Koren, H. S.; Devlin, R.; Graham, D.; Mann, R.; Horstman, D. H.; Kozumbo, W. J.; Becker, S.; McDonnell,
       W. F. (1989) Cellular and biochemical changes in the lower airways of subject- exposed to ozone,  In:
       Minister, W. G., ed., Proceedings of international symposium on the alveolar macrophage.

Koren, H. S.; Devlin, R.; Graham, D.; Mann, R.; McGee, M. P.; Horstman, D. H.; Kozumbo, W. J.; Becker,
       S.; House, D. E.; McDonneU, W. F.; Bromberg, P. A. (1989) Ozone-induced inflammation in the lower
       airways of human subjects.  Am. Rev. Resp. Dis. 139:  407-415  .

Lebret, E.; McCarthy, J.; Spengler, J.; Chang,  B. -H. (1987) Elemental composition of indoor fine particles. In:
       Seifert, B.; Esdom, H.; Fischer, M.; Rueden, H.; Wegner, J., eds., Indoor air '87: proceedings of the 4th
       international conference on indoor air quality and climate, v. 1, volatile organic compounds, combustion
       gases, particles and fibres, microbiological agents; August; Berlin, Federal Republic of Germany. Institute
       for Water, Soil and Air Hygiene; pp. 569-575,

Lewtas, J. (1989) Environmental monitoring using genetic bioassays.  In: Li, A. P.  and Helflich, R. H., eds.,
       Genetic toxicology: A treatise. The Teleford Press, Caldwell, NJ., U. S. Environmental Protection Agency,
       Health Effects Research Laboratory, Research Triangle Park, NC. EPA 600/D-89/I46.

Lewtas, J. (1989) Human Exposure and dosimetry of environmental tobacco smoke.  U. S. Environmental Protection
       Agency, Health Effects Research Laboratory, Research Triangle Park, NC.  HERL-0681.

Lewtas, J. (1988) Report on the use of biochemical and btoassay markers of exposure to environmental tobacco
       smoke in children,  U. S. Environmental Protection Agency, Health Effects Research Laboratory, Research
       Triangle Park, NC. EPA 600/X-88/303. HERL-0642.

Lewtas, J. (1989) Toxicology of complex mixtures of indoor air pollutants.  In:  George,  R.; Okuh, R.; Cho, A.
       K., eds., Annual review of pharmacology and toxicology 29:415-439.  EPA 6007 D-89/243.

Lewtas, J.; Goto, S.; Williams, K.; Chuang, J.  C.; Petersen, B. A.;  Wilson, N. K.  (1987) The mutagenicity of
       indoor air particles in a residential pilot  field  study:  Application and evaluation  of new methodologies.
       Atmos. Environ. 21(2): 443-449.
                                                  31

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Lewtas, J.; Goto, S.J Williams, K.; Chapel), J.; Wilson, N. K. (1987) Mutageoicity of indoor air in a residential
       field study. Environ. Mutagenesis 9: 58-59.

Lewtas, J.; Claxton, L. D.; Mumford, J. L. (1987) Human exposure to mutagens from indoor combustion sources.
       In: Seifert, B.; Esdora, H.; Fischer, M.; Ruedeo, H.; Wegner, J., eds., Indoor air '87:  Proceedings of the
       4th international conference on indoor air quality and climate, v. 1, volatile organic compounds, combustion
       gases, particles and fibres, microbiological agents, August, Berlin, Federal Republic of Germany.  Institute
       for Water, Soil and Air Hygiene; pp. 473-478.

Lewtas, J.; Clazton,  L. D.; Mumford, J. L.; Lofroth, G. (1990) Bioassay of complex mixtures of indoor air
       pollutants.  IARC, Indoor Air; vol  12; chapter 7, in press.

Lewtas, J.; Williams, K; Lofroth,  G.;  Hammond, K.; Leaderer,  B. (1987) Environmental tobacco smoke:
       Mutagenic emission rates and their relationship to other emission factors.  In:  Seifert, B.; Esdorn, H.;
       Fischer, M.; Rueden, H.; Wegner, J., eds., Indoor air '87:  Proceedings of the 4th international conference
       on indoor air quality and climate, v. 2, environmental tobacco smoke, multicomponent studies, radon, sick
       buildings, odours and irritants, hyperreactivities and allergies, August, Berlin, Federal Republic of Germany.
       Institute for Water, Soil and Air Hygiene; pp. 8-13.

Ling, P. L; Lofroth,  G.; Lewtas, J. (1988) Mutagenic determination of passive smoking. Toxicology Lett. 35:
       147-151.

Lofroth, G.; Burton, R.;  Forehand, L.; Hammond, S. 1C; Selai,  R.;  Zweidinger,  R.; Lewtas,  J.  (1989)
       Characterization of environmental tobacco smoke.  Environmental Science and Technology 23: 610-614.

Mattson, M. E.; Boyd, G.; Byar, D.; Brown, C; Callahan, J. F.; Corle, D'; CuUen, J. W.; Greenblatt, J.;
       Haley, N. J.;  Hammond, S. K; Lewtas, J.; Reeves, W- (1989) Passive smoking on commercial airline
       flights.  Journal of the American Medical Association 261(6):  867-872.

McCarthy, J.; Spengler, J.; Chang, B. -H.; Coultas, D.; Samet, J. (1987) A personal monitoring study to assess
       exposure to environmental  tobacco smoke. In:  Seifert, B.; Esdorn, H.; Fischer, M.; Rueden, H.; Wegner,
       J., eds., Indoor air '87:  Proceedings of the 4th international conference on indoor air quality and climate.
       v. 2, environmental tobacco smoke, multicomponent studies, radon, sick buildings, odours and irritants,
       hyperreactivities and allergies, August, Berlin, Federal Republic of Germany. Institute for Water, Soil and
       Air Hygiene; pp.  142-147.

McDonnell, W. F. (1989) Individual variability in the magnitude of acute respiratory responses to ozone exposure.
       hi: Utell, M.  J. and Frank, R., ed.. Susceptibility to inhaled pollutants, American Society for Testing and
       Materials, Philadelphia, PA.

McDonnell, W.  F. (1988) The respiratory effects of low-level ozone exposure:  clinical studies,  hi: Proceedings
       of the northeast regional environmental public health center's ozone risk communication conference, in
       press.

McGee,  M. P.; Devlin, R.; Koren, H.; Rothberger, H.  (1988)  Tissue factor and factor vii mma in alveolar
       macropbages.  Association with cell maturation shifts and evidence of clotting in alveolar exudants after
       breaming ozone.  Submitted to J. Clio. Invest.

Miller, F. J.; Overton, J.  H.; Gerrity, T. R.; Graham, R. C. (1988)  Interspecies dosimetry of reactive gases.
       In: Proceedings of ELSI conference on inhalation toxicology, Spriager-Verlag, NY, pp. 139-155.
                                                   32

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Morin, R, S.; Tulis, J. J.; Claxton, L. D. (1987) The effect of solvent and extraction methods on the bacterial
       mutagenicity of sidestream cigarette smoke. Tox. Letters 38: 279-290.  EPA 600/J-87/256.

Mumford J. L.; Chapman, R. S.; Harris, D. B.; He, X. Z.; Cao, S. R.; Xizn, Y. L.; Li, X. M. (1989) Indoor
       air exposure to coal and wood combustion emissions associated with a high lung cancer rate in Xuan Wei,
              Environment International 222: 81-99.
Mumford, J. L.; Chapman, R. S.; Nesnow, K. S.; Hebnes, C. T.; Li, X. (1989) Mutagenicity, carcinogenicity,
       and human cancer risk from indoor exposure to coal and wood combustion in Xuan Wei,  China.  In:
       proceedings of international conference on genetic toxicology of complex mixtures, July, Washington, DC.

Mumford, J. L.; He, X. Z.; Chapman, R. S.; Cao, D. S. R.; Harris, D. B.; Li, X. M.; Xian, Y. L.; Jiang,
       W. Z.; Xu, C. W.; Chuang, J. C.; Wilson, W. £.; Cooke, M. (1987) Lung cancer and indoor air pollution
       in Xuan Wei, China. Science 235: 217-220.

Mumford, J. L.; He, X. Z.; Chapman, R. S. (1990) Human lung cancer risks  due to complex  mixtures of
       combustion emissions. Recent Results in Cancer Research, in press.

Mumford, J. L.; Harris, D. B.; Williams,  K.; Chuaiig, J. C.; Cooke, M. (1987) Indoor air sampling and
       mutagenicity studies of emissions from unvented coal combustion. Environmental Science and Technology
       21: 308-311.

Mumford, J. L.; Helmes, C.  T.; Lee, X.; Seidenberg, J.; Nesnow, S. (1990) Mouse skin tumorigenicity studies
       of indoor coal and wood combustion emissions from homes, of residents in Xuan Wei, China with high lung
       cancer mortality. Carcinogenesis, in press.

Mumford. J. L.; Lewtas, J.;  Burton, R. M.; Henderson,  F. W.; Forehand, L.; Allison, J. C.; Hammond, K.
       S. (1989) Assessing  environmental tobacco smoke exposure of pre-school children in homes by monitoring
       air particles, mutagenicity, and nicotine. In: Proceeding of the 1989 EPA/A&WMA international symposium
       on measurement of toxic and  related air pollutants, Raleigh, NC,  pp. 606-610.

Mumford, J. L; Williams, K. (1986) Indoor air sampling and mutagenicity  studies related to  emissions from
       unvented coal combustion.   In:   Proceedings of 79th air pollution control association annual meeting-
       exhibition, Minneapolis, MN 86-6.5:  1-13.

Orlando, G.; Hose, D.; Koren, H.;  Becker, S, (1988) Effect of ozone on  T cell proliferation and neurohormone
       levels in exercising males. .Inhalation Toxicol., in press.

Otto, D.; Molhave, L.; Rose, G.; Hudnell, K.; House, D. (1990) Neurobehavioral and sensory irritant effects of
       controlled exposure to  a complex mixture of volatile organic compounds. Submitted to: Neurotox. Teratol.

Quackenboss, J. J.; Lebowitz, M. D.; Cnitchfield, C. D.; Burtchin, D. (1988) Indoor-outdoor relationships for
       particulate matter and verification of exposure classification, hi:  Seifert, B.; Esdorn, H.; Fischer,  M.;
       Rueden, H.; Wegner, J., eds., Indoor air '87:  Proceedings of the 4th international conference on indoor
       air quality and  climate,  v.  1,  volatile organic compounds, combustion  gases, particles  and fibres,
       microbiological agents, August,  Berlin, Federal  Republic of Germany. Institute for Water, Soil and Air
       Hygiene; pp.  534-539.
                                                  33

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Quackenboss, J. J.; Lebowitz, M.  D.;  Hayes, C.  (1988) Epidemiological study of respiratory responses to
       indoor/outdoor air quality. In: Seifert, B.; Esdom, H.; Fischer, M.; Rueden, H.; Wegner, J., eds., Indoor
       air '87: Proceedings of the 4th international conference on indoor air quality and climate, v. 2, environ-
       mental tobacco smoke, multicornponent studies, radon, sick buildings, odours and irritants, byperreactivities
       and allergies, August, Berlin, Federal Republic of Germany. Institute for Water, Soil and Air Hygiene; pp.
       198-203.

Quackenboss, J. J.; Lebowitz, M. D.; Bronnimann, D.; Michaud, J. P. (1988) Formaldehyde exposure and acute
       health effects study. In: Seifert, B.; Esdom, H.; Fischer, M.; Rueden, H.; Wegner, J., eds. Indoor air '87:
       Proceedings of die 4th international conference on indoor air quality and climate, v. 2, environmental tobacco
       smoke, multicomponent studies, radon, sick buildings, odours and irritants, hyperreactivities and allergies;
       August; Berlin,  Federal Republic of Germany.  Institute for Water, Soil and Air Hygiene; pp. 615*620.

Spengler, J. D.; Ware, J.; Spdtzer,  F.; Ferris, B.; Dockery, D.; Lebret, £.; Bninekreef,  B. (1988) Harvard's
       indoor air quality respiratory health study. In:  Seifert, B.; Esdom, H.; Fischer, M.; Rueden, H.; Wegner,
       J., eds. Indoor air '87: Proceedings of the 4th international conference on indoor air quality and climate.
       v. 2,  environmental tobacco smoke,  multicomponent studies, radon, sick buildings, odours and irritants,
       hyperreactivities and allergies; August; Berlin,  Federal Republic of Germany. Institute for Water, Soil and
       Air Hygiene; pp.  218-225.

Traynor, G. W.; Apte, M. G.; Sokol, H. A.; Chuartg, J. C.; Mumford, J. L. (1986) Selected organic pollutant
       emissions from unvented kerosene heaters. In:  Proceedings of 79th air pollution control association annual
       meeting-exhibition 86-52.5:  1-20.

Traynor, G. W.; Apte, M. G.; Sokol, H. A.; Chuang, J. C.; Tucker, W. G.; Mumford, J. L. (1990) Selected
       organic pollutant emissions from unvented kerosene heaters,  Environ. Sci. Tech., in  press.

Watts, R.; Langone, J.; Knight, G.; Levrtas, J. (1990) Cotinine analytical workshop report:  Consideration of
       analytical methods for determining cotinine in human body fluids as a measure of passive exposure to tobacco
       smoke.  Environ. Health Perspect., in press.

White, J. B.; Leaderer, B. P.; Boone, P. M.; Hammond, S. K.; Mumford, J. L. (1987) Chamber studies
       characterizing organic emissions from kerosene space heaters.  In:  Proceedings of the 1987 EPA/APCA
       symposium on measurement of toxic and related air pollutants.  Pittsburgh, PA.  pp. 98-103.

Williams, R. W.; Pasley, T.; Watts, R.; Inmon, J.; Fitzgerald, J.; Claxton, L. (1989) Comparative yields of
       mutagens from  cigarette smokers' urine obtained by using  solid-phase extraction techniques.  Environ.
       Molecular Mutat. 14: 20-26, U. S. Environmental Protection Agency, Health Effects Research Laboratory,
       Research Triangle Park, NC, EPA 600/J-89/223.
                                                   34

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PRESENTATIONS AND OTHER REPORTS
Benignus, V. A. (1987) Neurotoxic effects of mixtures of air pollutants. Presented at the Effects of Fin Products
       on Psycho Performance on Surface Ships; November; Groton, CT.

Devlin, R.; Noah, T.; McKnnon, K.; Scott, M. V.; Korea, H. (1990) The use of a cell line as a model system
       to study the interaction of environmental toxicants with human airway epithelial cells.  To be Presented at
       the UCLA Symposium, Los Angeles, CA.

Goldstein, G. M; Collier, A.; Shrewsbury, R. (1989) The use of cotinine as a biomarker of ETS exposure in young
       children. Presented at the International Indoor Air Quality and Ventilation Conference, Lisbon, Portugal and
       to be Presented at the 5th International Conference on Indoor Air Quality and Climate, Toronto, Canada.

Goto, S.; Lewtas, J.; Matsushita, H. (1989) Mutation assay for personal airborne paniculate samples by a highly
       sensitive ultra-micro  forward-mutation method.    Presented at the 5th  International Conference  of
       Environmental Mutagens, Cleveland, OH.

Goto, S.; Matsushita, H. (1989) Microsuspension assay using a new Salmonella typhimurium strain for the
       evaluation of mutagenicity of airborne participates indoors.  Presented at the Symposium on Genetic
       Toxicology of Complex Mixtures, Washington, DC.

Goto, S.; Matsushita, H.; Williams, K.; Demarini, D. M.; Lewtas, J.; Takagi, Y.j Murata, M. (1988) Assay
       and application to airborne particulates collected by personal samplers. U. S. EPA In-house.

Korea, H. S.; Graham, D. E.; Steingold, S.; Devlin, R. (1990) The inflammatory response of the human upper
       airways to volatile organic compounds (VOC). To be Presented at the American Thoracic Society Meeting,
       Boston,  MA.

Korea, H.; Graham, D.; Steingold, S.; O'Neil, J.; Devlin, R. (1990) The inflammatory response of the human
       upper airways to volatile organic compounds (VOC). To be Presented at the 5th International Meeting on
       Indoor Air Quality and Climate, Toronto, CA.

Levine, J. G.; DeMarini, D. M. (1990) Induction of revertants of the HISD3052 allele of Salmonella typhimurium
       TA98 in cigarette smoke condensate and analysis  by the polymerase chain reaction and  direct DNA
       sequencing. To be Presented at the Environmental Mutagen Society Meeting, Albuquerque, NM.
                          \
Lewtas, J.; Goto, S.; Williams, K.; Chappell, J.; Wilson, N. (1987) Mutagenicity of indoor air in a residential
       field study. Presented at the Environmental Mutagen Society  Meeting; April; San  Francisco, CA.

Lofroth, G.; Burton, B.; Goldstein, G.; Forehand, L.; Hammond, K.; Mumford, J.; Seila, R.; Lewtas, J.
       (1987) Genotoxic emission factors  for  sidestream cigarette  smoke  components.   Presented  at  the
       Environmental Mutagen Society Meeting; April; San Francisco, CA.

Monteith, L. G.; Myers, C. B.; Simmons, D. S.; Hughes, T. J.; Claxton, L. D. (1987) Comparative genotoxtciry
       of sidestream and mainstream cigarette smoke.  Presented at the Environmental Mutagen Society Meeting;
       April; San Francisco, CA.
                                                 35

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Mumford, J. L.; Chapman, R. S.; Nesnow, K. S.; Hebnes, C. T.j Rudd, C. J.; Li, X. (1989) Mutagenicity,
       carcioogeaicity, and human cancer risk from indoor exposure to coal and wood combustion in Xuan Wei,
       China. Presented at the 1989 International Conference on Genetic Toxicology of Complex Mixtures.

Mumford, J. L.; Lewtas, J.; Henderson,  F. W.j Hammond, K. S. (1990) Assessing mutagen exposure from
       environmental tobacco smoke in pre-school children's homes. To be presented at the Environmental Mutagen
       Society Meeting, Albuquerque, MM.

Mumford, J.; Walsh, D.; Burton, R.; Svendsgaard, D.; Chuang, J.; Lewtas, J.; Houk, V.; Williams, R. (1990)
       Unvented kerosene heater emission in mobile homes: Studies on indoor air particles, semi-volatile organics,
       carbon monoxide and nmtageaicity.  To be Presented at the 5th International Conference on Indoor Air
       Quality and Climate, Toronto. Canada.

Noah, T. L.; Devlin, R. B.; McKumon, K.; Scott, M. V.; Koran, H. S. (1990) The use of an epithelial cell line
       as a model system to study the effects of ozone on human airway epithelium in vitro. To be Presented at the
       American Thoracic Society Meeting, Boston, MA.                                                '

Otto, D.; Hudnell, K.; Counts, W. (1990)  Application of computerized behavioral tests in controlled human
       exposure studies. To be Presented at the 5th International Conference on Indoor Air Quality and Climate,
       Toronto, Canada.

Otto, D.; Hudnell, K.; Molhare, L. (1990) Temporal differences in olfactory and trigeminal symptom response to
       a complex mixture of volatile organic compounds.  To be Presented at the 5th International Conference on
       Indoor Air Quality  and Climate,  Toronto, Canada.

Otto, D.; Molhave, L.; Rose, G.; Hudnell, H. K.; House, D. (1989) Neurobehavioral and sensory irritant effects
       of controlled exposure to a complex mixture of volatile organic compounds. Presented at the 7th International
       Neurotoxicology Conference, Little Rock, AK.

Otto, D.; Rose, G.; Hudnell, K.; House, D. (1989)  Neurobehavioral and sensory irritant effects of controlled
       exposure to a complex mixture of volatile organic compounds. Presented at the 2nd Meeting of International
       Neurotoxicology Association, Citges, Spain.

Otto, D. (1989) Sensory irritant and neurobehavioral impacts of exposure to low levels of VOCs.  Presented  at the
       Quarterly Meeting of Interagency Committee on Indoor Air Quality (CIAQ), Washington, DC.

Quackenboss, J. J.;  Lebowitz,  M.  D.; Camilli, A. £.; Hayes, C. (1987) Multipollutant  (indoor-outdoor)
       interactions and health.  Presented at the  80th Annual Meeting of the Air Pollution Control Association;
       June; New York, NY.

Walsh,  D. B.; Claxton, L. D.  (1990) Structure activity analysis of azo dyes by specific salmonella strains
       mutagenicity.  To be Presented at the  Environmental Mutagen Society Meeting, Albuquerque, NM.

Waters, M. D. (1989) Genetic toxicology of complex mixtures-overview and summary of the Washington satellite
       meeting. Presented at the 5th International Conference on Environmental Mutagens, Cleveland, OH.
                                                  36

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APPENDIX C

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PROTECTION AGENCY ''
        PLAN (FY90-94)

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      INDOOR AIR RESEARCH FIVE-YEAR PLAN (FY90-94)
                                CONTENTS



I.   INTRODUCTION

H.  GENERAL DIRECTION OF RESEARCH AND FUTURE GOALS

    A.    Indoor Air Monitoring and Building Studies

    B.    Indoor Air Health Effects

    C.    Indoor Air Source Characterization and Mitigation

    D.    Indoor Air Health Impact and Risk Assessment

    E.    Indoor Air Program Management and Technology Transfer

m. SUMMARY OF RESEARCH AREAS SUPPORTING
    MAJOR PROGRAMMATIC NEEDS BY LABORATORY

    A.    Program Need No. 1: Characterize Exposure and Health Effects of
          Chemical Contaminants and Pollutant Mixtures Commonly Found
          Indoors

    B.    Program Need 2: Characterize and Develop Mitigation Strategies for
          Biological Contaminants

    C.    Program Need 3: Characterize Significant Indoor Air Pollution
          Sources and Evaluate Appropriate Mitigation Strategies

    D.    Program Need 4: Develop and Promote Guidelines Covering
          Ventilation as Well as Other Building Design, and Maintenance
          Practices for Ensuring That Indoor Air Quality is Protective
          of Public Health

    E.    Program Need 5: Information Dissemination

    F.    Program Need 6: Indoor Air Quality Problems in Buildings
Page

  1

  2

  2

  3

  4

  5

  6
  9

  9

 10

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     INDOOR AIR RESEARCH FIVE-YEAR PLAN (FY90-94)
                               TABLES
A.  INDOOR AIR RESEARCH PRIORITIES BY LABORATORY

    1.    Air and Energy Engineering Research Laboratory - Monitoring
         and Building Studies
                               i
    2.    Air and Energy Engineering Research Laboratory - Source
         Assessment & Mitigation

    3.    Health Effects Research Laboratory - Health Effects Research

    4.    Environmental Criteria and Assessment Office - Health
         Impact Risk Assessment
Page


 10


 10


 12

 14


 15
B.  CURRENT INDOOR AIR RESEARCH ACTIVITIES IN
    PRIORITY ORDER

    GROWTH AREA RESEARCH IN PRIORITY ORDER
 17

 17
                                  11

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      INDOOR AIR RESEARCH FIVE-YEAR PLAN (FY90-94)
L    INTRODUCTION

     Title IV of the Superfund Amendments and Reauthorization Act of 1986 (SARA) requires
     the Environmental Protection Agency to establish a research program with respect to radon
     gas and indoor air quality and to disseminate information on indoor air quality problems
     and solutions.  In a recent report to Congress, EPA noted that indoor air research and
     policy  programs  have not sufficiently  characterized indoor air quality  problems and
     solutions to be  able to determine health effects, appropriate mitigation recommendations,
     or the need for possible regulatory actions.  EPA made six recommendations intended to
     develop the necessary information to make such determinations.  These recommendations
     are listed below and represent the primary objectives, activity, and support areas of EPA's
     Indoor Air Research Program for the next five years.

     1.. Research to better characterize exposure and health effects of chemical contaminants and
        pollutant mixtures commonly found indoors should be significantly expanded.

     2. A research program to characterize and develop mitigation strategies for biological
        contaminants in indoor air should be developed.
                                      •
     3. Research to identify and characterize significant indoor  air pollution sources and to
        evaluate appropriate mitigation strategies should be significantly expanded.

     4. A program  is needed to develop and promote, in conjunction with appropriate private
        sector organizations, guidelines covering ventilation, as well as other budding design,
        operation, and maintenance practices for ensuring that indoor air quality is protective
        of public health.

     5. A program of technical assistance and information dissemination, similar  in scope to
        the Agency's radon program, is needed to inform the public about risks and mitigation
        strategies, and to assist state and local governments and  the private sector in solving
        indoor air quality problems. Such a program should include an indoor air quality
        clearinghouse.

     6. The Federal government should undertake an effort to  characterize the  nature and
        pervasiveness of the health impacts associated with indoor air quality problems in
        commercial and public buildings, schools, health care facilities, and residences, and
        develop and promote recommended guidelines for  diagnosing and  controlling  such
        problems.

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O.   GENERAL DIRECTION OF RESEARCH AND FUTURE GOALS

     To support the general goals and needs of EPA's Indoor Air Program, the Agency's Indoor
     Air Research Program is organized around the following areas: Indoor Air Monitoring and
     Building  Studies;  Indoor Air Health Effects; Indoor Air Source Characterization and
     Mitigation;  Indoor Air Health  Impact and Risk Assessment; and Indoor Air Program
     Management and Technology Transfer.

     The general goals and direction of research during the next five  years in each of these
     areas is summarized below.

     A.    Indoor Air Monitoring and Building Studies:
               i
     The goals of the monitoring and building studies program are to:

           1) Develop and validate building diagnostic protocols;

           2) Conduct indoor air investigations and demonstration studies;

           3) Develop and  validate microenvironmental, personal exposure,  and  passive
              monitors;

           4) Develop and validate analytical techniques;   .

           5) Develop, publish, and  distribute a  compendium containing  state-of-the-art
              protocols for indoor air investigations;

           6) Develop indoor air quality assurance reference materials;

           7) Develop exposure assessment  protocols  to  include standardized   survey
              questionnaires, personal activity logs, and procedures relating exposures to
              individual source strengths;

           8) Develop and validate comprehensive indoor air models for large buildings; and

           9) Coordinate and maintain a comprehensive data base containing validated results
              from indoor air investigations and baseline results from large scale noncomplaint
              and high complaint building studies.

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 In the area of building diagnostics and large building studies, the program will be moving
 toward integrated protocols,  the study of multiple pollutants, and the coordination of
 physical examination, monitoring,  analysis, and exposure assessment procedures.   The
 program will emphasize the collection of baseline data under different building structure
 conditions and environmental variations for both complaint and noncomplaint buildings.
 The large building  model will be  incorporated into building  studies to aid in the
 investigation of building designs and mitigation options.  The building  investigations
 program will be moving away from studies of single parameters and single time periods and
 the development of stand-alone modeling concepts.

 In the area of monitoring  and analytical methods development the program is headed
 towards integrated sampling  systems requiring minimal  resources, biological  methods
 development, and passive monitoring devices to be used as screening tools. The monitoring
 development program will enlarge and enhance the compendium of methods by increasing
 the number of protocols and pollutant species and by preparing an abbreviated edition for
 technicians.  The monitoring program will move away from the development of large,
 single parameter instruments and the development of samples for nicotine.

 B.    Indoor Air Health Effects:

 The health effects indoor air research program is multidisciplinary in scope involving the
 Human Studies,  Genetic Toxicology, Neurotoxicology, and Environmental Toxicology
.Divisions of HERLand is coordinated with engineering and monitoring activities of Air and
 Energy  Engineering Research Laboratory (AEERL) and  Atmospheric  Research and
 Exposure  Assessment  Laboratory  (AREAL)  and  the  risk  assessment  activities of
 Environmental Criteria and Assessment Office (ECAO).

 The primary goals of indoor air health research are to:

 1)  Identify or develop sensitive functional or physiological  measures to characterize the
    health effects of exposure to indoor air pollutants;

 2)  Determine the comparative irritancy and response thresholds of indoor air pollutant
    chemicals and mixtures;

 3)  Identify and characterize chemically sensitive individuals and population subgroups
    susceptible to sick building syndrome;

 4)  Develop and apply biomarkers of inflammation and allergy in upper airways following
    exposure to indoor air pollutants;

 5)  Develop  and apply biomarkers for exposure and dosimetry assessment of indoor
    carcinogens;

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6) Evaluate the effectiveness of air cleaners for reducing mutagenicity indoors;

7) Characterize  the  mutagenicity and carcinogenicity of complex mixtures of indoor
   pollutants and identify major sources;

8) Develop and  apply methods for biomonitoring the potential carcinogenicity of indoor
   volatile organic compounds (VOCs); and

9) Conduct cross-species extrapolation studies necessary for risk assessment of indoor air
   pollutants.

Indoor air health effects studies are currently focussed on controlled laboratory studies of
the neurotoxic,  inflammatory, allergic, and pulmonary  effects of VOC mixtures,
environmental tobacco smoke  (ETS), and combustion  products.  The objectives are to
identify and  characterize the health effects of ETS, VOCs, and combustion products
commonly found in the indoor environment.   Results of preliminary work  indicate
subjective reactions to VOC exposure, but no consistent pattern of neurobehavioral effects.
There is preliminary evidence of inflammatory effects of VOC exposure.  Identification of
reproducible functional or physiological effects of VOC exposure is necessary before field
studies of "sick" building  occupants can be undertaken.  Development of an objective
method to identify chemically sensitive individuals is a high priority. Collaborative studies
with the Engineering Program to characterize the health effects of exposure to real-world
product emissions are  projected to begin in  FY91.   Parallel  animal model studies to
characterize dose-response relationships  and physiological mechanisms of indoor health
effects are projected to begin in FY92.

The Health Effects Research Laboratory (HERL) has investigated the mutagenicity of indoor
combustion emissions, including ETS and kerosene heater emissions, in  chambers and
homes.  Tobacco smoke was  found to be a primary source of indoor mutagens.  Dosimetry
studies: of cotinine in preschool children were also performed  to develop a method for
assessing  ETS exposure  in children.    Kerosene heaters  were found  to  emit  high
concentrations of semivolatile  organics and to emit mutagenic  particles  containing  nitro
PAH.  The general direction and goals of future research are to  1) assess the genotoxicity
of indoor  air, identify the  genotoxic  components, and identify the main  sources of
mutagens; and to 2) characterize and assess human exposure to indoor carcinogens by using
biomarkers for cancer risk assessment.

C.    Indoor Air Source Characterization and Mitigation:

The primary goals of the Indoor Air Source Characterization and Mitigation Program are
to:

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      1) Develop methods for measuring pollutant emission rates and models to predict
         exposure;

      2) Gain an understanding of sorption and reemissions from "sinks";

      3) Develop methods for directly measuring sensory irritation from sources;

      4) Enlarge EPA's data base on sources and emissions;

      5) Develop methods for  evaluating air cleaners, source control options,  and
         ventilation strategies; and

      6) Develop and demonstrate IAQ models for comparing control options.

The  source evaluation program is  moving toward developing information on  "clean"
materials and products.  This includes product testing for chemical emissions, response-
based testing with animals or humans, and the marketplace involvement of manufacturers
and consumers. Also a move will be made toward better understanding the role of pollutant
sinks as emitters. As EPA methods are made available, the program will move away from
the development of methods for measuring emission rates from sources.

An important new thrust of the indoor air research program is in the area of IAQ control.
In this area the program is moving toward the development of design information on
effective ventilation, the evaluation of air cleaners and source management options, and
control options for biocontaminants. The program will move away from controlled studies
and will emphasize more field work.

D.    Indoor Air Health Impact and Risk Assessment:

The  overall goal of risk assessment  is to describe and prioritize the various health effects
encountered indoors.  Methodologies will  be improved to assess health impacts and risks
of poor indoor air quality in relation to multiple pollutants and multiple health endpoints.
EPA's risk/health impact  characterization framework will  be greatly enhanced using
personal computer software and more accurate exposure estimates.  A detailed assessment
of biocontaminants found indoors will be conducted.  Risk assessments will be conducted
for specific carcinogenic compound mixtures found indoors.  Common indoor air quality
scenarios will be evaluated to assess noncancer or nonfatal effects of indoor exposures
with emphasis on occupational sensitivity and productivity. The assessment program will
move away from death and cancer  as the only indoor air endpoints and will emphasize
noncancer effects and  multiple pollutants.

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E.    Indoor Air Program Management and Technology Transfer:

The management goal of the Indoor Air Research Program will continue to emphasize close
coordination with the Office of Air and Radiation (OAR) Indoor Air Division; coordination
with Federal agencies in planning and conducting research; assistance to the private sector
in development of indoor air research programs; multidisciplinary involvement in research
projects and assessment; and state-of-the-art management systems for coordination within
EPA, for timely information dissemination, and for effective project tracking. Support will
be given to national meetings concerned with indoor air quality.

SUMMARY OF RESEARCH AREAS SUPPORTING MAJOR PROGRAMMATIC
NEEDS BY LABORATORY                                |

A.    Program Need No. 1: Characterize Exposure and  Health1 Effects of Chemical
      Contaminants and Pollutant Mixtures Commonly Found Indoors

Atmospheric Research and Exposure Assessment Laboratory:

New and improved monitoring and analytical methods will be developed in support of the
Indoor Air Program. Emphasis will be placed on air exchange rate, environmental tobacco
smoke,  volatile and  semivolatile  organic compounds,   and  bioaerosol  techniques.
Monitoring methods development will be directed to developing new microenvironmental,
personal exposure, and passive techniques.  Integrated samplers capable of  screening
multiple pollutants will also be designed and evaluated. The monitor designs will  stress low
resource requirements,  high species selectivity,  high collection efficiencies,  and high
reproducibility.  New analytical methods will be developed for the collection, extraction,
and analysis of each species  listed above.  In addition, continued emphasis will  be placed
on  the  analysis of polar volatile and semivolatile organic compounds  because these
substances  are  associated with the highly  toxic sample  fractions.   Components of
environmental tobacco smoke and probable tracer gas analyses will also be examined.
Analytical methods development research will stress improved sensitivity, reproducibility,
and selectivity with minimum cost.

Health Effects Research Laboratory:

Human  clinical  exposure studies will be performed to identify behavioral, physiological,
neurochemical, inflammatory, and allergic responses which  characterize health  effects of
indoor air pollution. The comparative irritancy and thresholds of individual or mixtures of
real-world, indoor air pollution products (as determined by AEERL and AREAL) will be
studied. A major focus will be to identify individuals or populations sensitive to  indoor air
pollution.  These data will allow the agency to predict and to validate human responses to
common indoor air pollutants in order to mitigate and to prevent sick building syndrome.

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              Criteria and Asessment Office:
Health assessment methodologies will continue to be developed for multiple pollutants
(mixtures) and noncancer endpoints.  Assessments  will be conducted for sources and
mixtures identified by the health and sources evaluation programs.  Example assessments
might be for carpet, kerosene heaters, or specific compounds such as 1,3-butadiene.

Air and Energy Engineering Research Laboratory:

The primary objective of EPA's source assessment is to identify the various compounds
emitted from products used  indoors and to estimate concentrations to which humans are
exposed.  Research will continue to develop  methodologies for source testing.  EPA's
indoor air model will  be continuously improved to realistically evaluate human exposures.
B.    Program Need 2: Characterize and Develop Mitigation Strategies for Biological
      Contaminants.

Environmental Criteria and Assessment Office:

A formal health assessment of biocontaminants found indoors will begin in FY90.  The
assessment will address the sources and species of biocontaminants found indoors; evaluate
the  transport and fate of these contaminants; and describe known health effects.  Where
possible, mitigation principles will be recommended.

Atmospheric Research and Exposure Assessment Laboratory:

In FY90 the monitoring program will begin to plan and implement a program for the
detection and identification of biocontaminants found indoors.  During the period FY91-
94,  protocols for monitoring biocontaminants will be developed and made a part of EPA's
compendium of indoor air sampling methods.

Air and Energy Engineering Research Laboratory:

In FY91, evaluation of the growth and control of biocontaminants will become an integral
part of EPA's mitigation research program. The objective of the research will be to
understand the effect of environmental and source conditions on biocontaminants growth
and viability on indoor materials especially  those found in ventilation and air handling
systems. One additional purpose of the research is to develop ASTM or ASHRAE standard
methods for testing performance of air cleaners in reducing  biocontaminant exposures
especially in such environments as schools, medical facilities, and large offices.

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C.    Program Need 3:  Characterize Significant Indoor Air Pollution Sources and
      Evaluate Appropriate Mitigation Strategies.

Health Effects Research Laboratory:

Hie Indoor Air Health Research Program will emphasize the effects of VOC mixtures on
neurobehavioral and physiologic effects in humans, and the establishment of an animal
inhalation exposure facility to assist in evaluating VOCs from indoor sources.  For VOCs
and chemical mixtures, a more realistic, and sensitive line of research is necessary. The
focus of the research is the hypersensitivity, neurotoxicity, and the annoying properties of
chemical mixtures. In ETS research, emphasis will be on determining the distribution of
constituents in the participate and vapor phases of ETS and identifying and evaluating
marker compounds for these two phases of ETS.                                  /,
                                     '                                         'di
Efforts will continue to assess human response to mixtures.  Biomarker research will
continue  to examine ways  cotinine can be used to estimate exposure to ETS.  Research
efforts will be expanded to emphasize the noncancer health effects using animal studies.
Assessments of the genotoxicity of emissions from various indoor combustion appliances
and associated mitigation strategies will be completed.  Studies will  better characterize
human response to the complex emission components of indoor sources.   The work will
help to identify potential sources of health hazard for more detailed investigation.

Air and Energy Engineering Research Laboratory:

Indoor source evaluations via small chamber testing will be continued  to focus on widely
used products that affect indoor air quality. Candidates for testing include: carpets, wall
coverings, paints, waxes/polishes, caulks, adhesives and reemitting sinks such as old carpets
and ductwork liners from heating, ventilating, and air conditioning  (HVAC) systems.
Expansion of source characterization research will include an in-depth evaluation of sensory
irritation  response in  a cooperative  project between  EPA's  Health  Effects Research
Laboratory  and the Engineering Laboratory. Mathematical models of source emissions and
"sink effects" will be developed.  They will be incorporated into the IAQ model, which will
be further enhanced by improving the user interface and increasing the speed of the solution
algorithms.  IAQ test house studies will focus on  fast decaying, solvent based products
(e.g., stains, varnishes, and waxes).  This research will provide information useful to
consumers on use practices that will reduce exposure to solvent emissions. Research on
air cleaners will focus on the development of appropriate testing methods for indoor particle
filters.  Cooperative  work with ASHRAE and other private organizations  will include
development  of  methods for determining ventilation  effectiveness.   An international
workshop on indoor source characterization will be conducted for the exchange of research
results with worldwide experts.   Technical support to EPA  Program Offices will be
provided as needed.
                                     8

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D.    Program Need 4: Develop and Promote Guidelines Covering Ventilation as Well
      as Other Building Design, and Maintenance Practices for Ensuring That Indoor
      Air Quality is Protective of Public Health.
Air and Energy Enineerin  Research 1
Prior to FY91 , only limited research will have been conducted to support indoor air quality
control and mitigation.  An expanded research program will be directed to designing and
evaluating control devices and mitigation strategies. Research on air cleaning devices will
be expanded by:  1) developing and testing improved designs for particle air cleaners;
2) conducting R&D on new concepts for removing vapor-phase organics from indoor air;
and 3) evaluating the cost-effectiveness of cleaning outdoor air used for ventilation in
situations  where it doesn't meet NAAQS's (a major problem for meeting ASHRAE
Standard 62 in some cities). This research will result in recommendations on air cleaners,
ventilation strategies, and  methods for modifying or  treating indoor sources to reduce
emissions.
£.    Program Need 5:  Information Dissemination.

Atmospheric Research and Exposure Assessment Laboratory:

The Indoor Air Monitoring and  Building Studies  Program will ^continue to emphasize
monitoring and analytical methods development,  building diagnostic and  remediation
methods, and technology transfer.  Monitoring and analytical methods development research
will include the development and evaluation of personal and microenvironmental monitors
for SVOCs and  polar  organic compounds; and the development of quality  assurance
standards for compounds  routinely measured indoors (e.g.,  nicotine and  semivolatile
compounds).  Research in building diagnostic and  remediation methods will include the
evaluation of indoor air quality data from large Federal buildings such as the Library of
Congress and  EPA/Waterside Mall buildings and the development and refinement of
procedures to evaluate large building exposure assessment and indoor air quality problems.
Technology transfer activities will include the publication of the compendium of indoor air
quality measurement methods.

Environmental Criteria and Assessment Office:

An expanded program will emphasize support of a major international technical conference
on  indoor air  pollution, the publication of a series  of technical  reports on indoor air
pollution; increased support and broader technical assistance to OAR, Regional Offices,
state and local governments. Emphasis will be given to the support of a national indoor air
clearing house that would include a body of technical information as represented by the
Research Program's Bibliographic Data Base.

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     F.    Program Need 6: Indoor Air Quality Problems in Buildings.

     Atmospheric Research and Exposure Assessment Laboratory!

     EPA's capability to study buildings will be greatly expanded. The building study program
     will apply diagnostic procedures developed by the research program and will integrate the
     monitoring and health  resources of the Agency in a coordinated effort to explain and
     evaluate environmental conditions and the status of health found indoors, especially in large
     buildings. Studies will  be conducted that evaluate both normal and complaint buildings so
     as to better predict when and the type of health problems that will likely occur in the
     presence of a particular indoor air quality scenario. Studies will also begin that evaluate
     the productivity of office workers exposed to unhealthy indoor air. Efforts will begin with
     other  Federal  agencies to  develop standardized methods! for measuring biological
     contaminants.  Procedures to investigate the contribution of !HVAC equipment to indoor
     biological contaminant levels will be developed.

     A formalized body of knowledge related to  building science will be developed.   The
     following will be initiated:  investigation of  potential sources and ventilation problems
     (preferably in Federally owned or  leased office building(s) with occupant complaints);
     development of corrective actions; implementation of corrective actions and evaluation of
     results; and establishment of guidelines for problem building evaluations and corrective
     actions.

 IV. TABLES
                                     TABLE A

            INDOOR AIR RESEARCH PRIORITIES BY LABORATORY


1.   Air and Energy Engineering Research Laboratory - Monitoring and Building Studies

                               CURRENT PRIORITIES

     a.     Developing building diagnostics protocols
     b.     Conduct of large building studies
     c.     Development of a compendium of indoor air methods
     d.     Development of monitoring methods
     e.     Development of analytical methods
     f.     Development of QA standard reference materials
     g.     Modeling of indoor air environments
     h.     Development of exposure assessment instruments/protocols
                                         10

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                          MOVING TOWARD

BUILDING DIAGNOSTICS

a.     Integrated protocols
b.     Incorporation of physical examination, monitoring, analysis, and exposure protocols
c.     Simultaneous collection of multiple pollutant, physical, and personal data
LARGE BUILDING STUDIES

a.

b.

COMPENDIUM
Collection of baseline data under multiple structure conditions, both complaint and
noncomplaint
Assessing seasonal variations
a.    Abbreviated edition for technicians
b.    Development of technical assistance document
c.    Increased number of protocols and species monitored
MONITORING METHODS.

a.    Integrated sampling systems requiring minimal resources
b.    Biological methods development
c.    Passive and screening devices

ANALYTICAL METHODS

a.    Development of routine methods for polar compounds
b.    Characterization of collection, extraction, and analysis parameters

QA STANDARDS

•     Development of QA reference materials for indoor air studies with emphasis on
      nicotine, SVOCs, and VOCs

MODELING

•     Incorporation of modeling into large building study designs and mitigation
                                   11

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EXPOSURE ASSESSMENT

a.     Development of standard survey instruments
b.     Development of standard activity logs

                           MOVING FROM

LARGE BUILDING STUDIES   }

a.     Conduct of studies for single parameters
b.     Conduct of studies for single1 time periods

MONITORING METHODS     jj

a.     Development of large, single parameter instruments
b.     Development of samplers for nicotine

MODELING

•     Development of stand-alone modeling concepts

Air and Energy Engineering Research Laboratory - Source Assessment & Mitigation

                        CURRENT PRIORITIES

a.     Methods for measuring pollutant emission rates
b.     IAQ modeling to predict exposures
c.     Pollutant sorption and reemission from sinks
d.     Methods for direct measurement of sensory irritation
e.     Data base on sources and emissions
f.     Methods for evaluating air cleaners
g.     Evaluations of air cleaners
h.     Evaluations of source control options
i.     Evaluations of ventilation strategies
j.     IAQ modeling to compare control options
                          MOVING TOWARD
SOURCE EVALUATION
a.    Developing information on "clean" materials and products
      - Product testing for chemical emissions
                                   12

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      - Response-based testing with animals or humans
      • Marketplace involvement (manufacturers, buyers)
b.    Understanding the role of pollutant sinks
      - Effect on short- and long-term exposures
      - Relationship to conditioned responses by occupants

MITIGATION & CONTROL

a.    Evaluating air cleaners
      - Test methods
      - Performance data:  particles, biocontaminants, gases
      - Marketplace involvement
b.    Developing design information on effective ventilation
      - Location of supply and return air registers
      - IAQ modeling to relate indoor sources to HVAC design
c.    Evaluating source management options
      - Product use practices
      - Material conditioning
      - IAQ modeling to evaluate exposure reductions
d.    Evaluating biocontaminant-specific control options
      - Humidity control systems
      - Biocides
e.    Evaluating sources and IAQ controls in the field
      - Demonstrate IAQ model in occupied buildings
      - Diagnose buildings for contaminant sources
      - Demonstrate IAQ control in occupied buildings

                             MOVING FROM

SOURCE EVALUATION

a.    Development of methods for measuring emission rates as EPA methods are being
      made available for use by private sector
b.    Exclusive focus on controlled studies
                                    13

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3.   Health Effects Research Laboratory - Health Effects Research
     a.    Develop  sensitive neurobehavioral,  neurochemical, inflammatory, allergic,  and
           pulmonary endpoints to characterize the health effects of exposure to indoor air
           pollutants
     b.    Identify and characterize chemically sensitive individuals and population subgroups
           susceptible to sick-building syndrome
     c.    Conduct  biomarker  studies of environmental tobacco smoke  (and other indoor
           sources) exposure in preschool children
     d.    Develop and apply bioassay methods for indoor volatiles
     e.    Determine comparative irritancy and health effect thresholds of indoor air pollutant
           chemicals and mixtures emitted by real-world building, cleaning, and personal care
           products
     f.    Assess mutagenicity of semivolatile and particle-phase organics in public buildings
     g.    Evaluate  the effectiveness of air cleaners for reducing mutagenicity indoors
     h.    Compare acute and chronic health effects of exposure to indoor air pollutants
     i.     Conduct cross-species extrapolation studies of acute and chronic effects of exposure
           to indoor air pollutants
                                 MOVING TOWARD
     HUMAN STUDIES
     a.     Chemical sensitivity evaluation
     b.     Realistic exposure concentrations related to widely used sources
     c.     Noncancer endpoints

     ANIMAL STUDIES

     a.     Source evaluation procedures
     b.     Irritation to upper airway passages

     BIOMARKERS

     a.     For exposure other than EPS
     b.     Mutagens in indoor air
                                          14

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                                 MOVING FROM

     HUMAN STUDIES

     a.    High concentration
     b.    Single pollutants

4.   Environmental Criteria and Assessment Office - Health Impact Risk Assessment

                              CURRENT PRIORITIES

     a.    Assessment methodology for multiple pollutants and noncancer endpoints
     b.    Assessment of biocontaminants
     c.    Indoor air quality effects data base
     d.    Bibliographic data base
     e.    Support of technical conferences
     f.    Simulation models for exposure assessment


                                MOVING TOWARD

     RISK ASSESSMENT METHODOLOGY

     a.    Multiple pollutants (mixtures)
     b.    Noncancer effects
     c.    Simulation models - PC based

     ASSESSMENTS

     a.    Biocontaminants
     b.    Public buildings - chemical reactions and upper respiratory disease
     c.    Toxic  indoor air contaminants  - pollutant  specific contributions  to  chemical
          sensitivity

     PROGRAM SUPPORT

     1.    Indoor air clearing house - technical information
     2.    Specialty  indoor air  research  workshops (control methods,  source assessment,
          assessment of biocontaminants)
                                        15

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                         MOVING FROM
RISK ASSESSMENT METHODOLOGY


a.    Single pollutants
b.    Death and cancer endpoints
             •

ASSESSMENTS


•    Individual carcinogens only
                               16

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                               TABLEB

CURRENT INDOOR AIR RESEARCH ACTIVITIES IN PRIORITY ORDER

a.    Methods for measuring pollutant emission rates
b.    Indoor air quality modeling to predict exposures
c.    Pollutant sorption and reemission from sinks
d.    Risk assessment methodology framework
e.    Indoor air quality effects data base
f.    Development of a compendium of indoor air methods
g.    Development of monitoring methods
h.    Development of analytical methods
i.    Evaluation of human response to VOC mixtures
j     ETS biomarker research
k.    Development of QA standard reference materials
1.    Modeling of large building environments
m.    Data base on sources and emissions
n.    Bibliographic data base
o.    Support of technical conferences

           GROWTH AREA RESEARCH IN PRIORITY ORDER

a.    Developing building diagnostics protocols
b.    Conduct of large building studies
c.    Assessment methods for multiple pollutants and noncancer endpoints
d.    Develop  sensitive neurobehavioral,  neurochemical, inflammatory, allergic,  and
      pulmonary  endpoints to characterize the health effects of exposure to indoor air
      pollutants
e.    Methods  for  direct measurement  of  sensory irritation from sources  - using
      animals/humans
f.    Identify and characterize chemically sensitive individuals and population subgroups
      susceptible  to sick-building syndrome
g.    Assessment of biocontaminants
h.    Methods for evaluating air cleaners
i.    Evaluations of source control options
j.    Evaluations of ventilation strategies
k.    IAQ modeling to compare control options.  Development of exposure assessment
      instruments/protocols simulation models for exposure assessment
1.    Conduct  biomarker studies of environmental  tobacco smoke (and other indoor
      sources) exposure in preschool children
m.    Develop and apply bioassay methods for indoor volatiles
                                    17

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o.    Determine comparative initancy and health effect thresholds of indoor air pollutant
      chemicals and mixtures emitted by real-world building, cleaning, and personal care
      products
o.    Assess mutagenicity of semivolatile and particle-phase organics in public buildings
p.    Evaluate the effectiveness of air cleaners for reducing mutagenicity indoors
q.    Compare acute and chronic health effects of exposure to indoor air pollutants
r.    Conduct cross-species extrapolation studies of acute and chronic effects of exposure
      to indoor air pollutants
                                      18

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APPENDIX D

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  ^OGRAMroR
1990' ":*=^r-; •;••;•>:£

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                 INDOOR AIR RESEARCH PROGRAM
                     FOR FISCAL YEAR 1990
                             CONTENTS
          INDOOR AIR PROGRAM MANAGEMENT & TECHNOLOGY
          TRANSFER

Project 1:   Indoor Air Program Management, Coordination and  Research
          Community Support

          INDOOR AIR HEALTH IMPACT AND RISK1 ASSESSMENT

Project 2:   Risk Characterization Methodology and Risk Assessment

Project 3:   Publication of the Indoor Air Reference Bibliography
 7

 9
          INDOOR AIR BUILDING STUDIES AND METHODS DEVELOPMENT  10
Project 4:   Computer Assisted Software for Upgraded NIST Indoor
          Dispersion/Ventilation Model

Project 5:   Quality Assurance Standards

Project 6:   Compendium of Indoor Air Quality Methods

Project 7:   Monitoring Methods Development

Project 8:   Analytical Methods Development

Project 9:   Large Building Studies
13

15

17

19

21

23

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           INDOOR AIR HEALTH EFFECTS                                 25

Project 10:  Neurobdiavioral,  Respiratory and  Sensory Irritant Effects of
           Complex VOC Mixtures in Humans                                 27

Project 11:  Biological Markers  for Environmental Tobacco Smoke (ETS)
           Exposure and Dosimetry in Children and Adults                        29

Project 12:  Toxicological Effects of VOC Mixtures in Animal  and In Vitro
           Systems                                                        32

           INDOOR ATR SOURCE CHARACTERIZATION AND MITIGATION    34
                             f
Project 13:  Indoor Air Source Characterization                                  38

Project 14:  Indoor Air Quality Control                                         40
                                      11

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     INDOOR AIR PROGRAM MANAGEMENT AND
                    TECHNOLOGY TRANSFER

FTEs
S&E
R&D
TOTAL
EYJ2
1.0
0.0
25.0
25.0
EI8J
1.0
60.0
30.0
90.0
FY89
1.0
60.0
22.0
82.0
FY90
1.0
58.2
75.0
133.2
FY91
1.0
103.0
42.0
145.0
Benefits to be Derived:

In responding to the requirements of indoor air legislation, EPA is undertaking a comprehensive
research and development effort through in-house work and in coordination with other Federal
agencies, state and local governments, and private sector organizations.  The ultimate goal of
SARA Title IV is to disseminate information to the public. Therefore, the central purpose of
EPA's Indoor Air Research Program is to provide timely information to identify and characterize
overall health risks in the indoor, environment and to reduce exposures that pose an .adverse
health risk. The objectives of the Program are to both determine the causes of excess risks and
to identify those activities and technologies that have the greatest potential for reducing risks and
significant health impacts.
Historical Perspectives:

In October 1986 Congress passed the Superfund Amendments and Reauthorization Act (SARA,
PL 99-499) that includes under Title IV "The Radon Gas and Indoor Air Quality Research Act".
The Act directs that EPA undertake a comprehensive indoor air research program.

Research program requirements under Superfund Title IV are specific. They call for EPA to
identify, characterize, and monitor (measure) the sources and levels of indoor air pollution;
develop instruments for indoor air quality data collection; and study high risk building types.
The statute also requires research to identify effects of indoor air pollution on human health.  In
the area of mitigation and control the Agency is to: develop mitigation measures to prevent or
abate indoor air pollution; demonstrate methods for reducing or eliminating indoor air pollution;
develop methods to assess the potential for soil gas contamination of new construction; and
examine design measures to avoid indoor air pollution.

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The EPA-ORD Indoor Air Research Program is organized around five categories of research:

      •     Program Management and Technology Transfer

      •     Risk Assessment

      •     Monitoring & Building Studies

I     *     Health Effects
 i
yj     •     Source Characterization
a
•«•
/Fiscal Year 1989:

Management of the Indoor Air Research Program will continue to emphasize close coordination
 with the  OAR  Indoor  Air Division; coordination  with Federal agencies  in  planning  and
conducting research;  multidisciplinary involvement in research projects and assessment;  and
 state-of-the-art management systems for coordination  within EPA,  for timely information
dissemination, and for effective project  tracking. Support will be given to national meetings
 concerned with indoor air quality.


 Fiscal Year 1990:

 An expanded program will emphasize support of a major international technical conference on
 indoor air pollution,  the publication of  a series of technical reports on indoor air pollution;
 increased support and broader technical assistance to OAR, regional offices, and state and local
 governments.
 Fiscal Year 1991:

 In addition to continuing the emphases given in FY89 and FY90, activities will include the
 design and public availability of a technical bulletin board.

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PROJECT 1:  INDOOR ADR PROGRAM MANAGEMENT, COORDINATION AND
              RESEARCH COMMUNITY SUPPORT

A.   Objectives:

     Manage the ORD Indoor Air Research Program by: coordinating the indoor air research
     efforts of participating ORD laboratories; coordinating the indoor air research activities of
     other  Federal  agencies; supporting  the  indoor  air research  community  through the
     preparation of  special  reports; sponsoring scientific  meetings;  and  publishing and
     disseminating technical information.

B.   Background:

     Title IV of the Superrund Amendments and Reauthorization Act of 1986 authorizes EPA
     to conduct an indoor air research program. It directs EPA to assure the public availability
     of the  findings of this research activity. Additionally, within the ORD Indoor Air Research
     Program, certain emerging issues and concerns are of sufficient interest to be investigated
     on a limited basis in order to determine if a larger research emphasis is warranted.

C.   Approach:

     The Matrix Manager directs the ORD Indoor Air Research Program through a steering
     committee that represents both the participating ORD laboratories and ORD Headquarters
     offices. The research program focuses on:  the risk assessment of indoor environments and
     conducts research in the areas of risk assessment methodology; monitoring; modeling and
     building studies; health effects; and source assessment and mitigation techniques.

     Other  specific projects are conducted under the direction of the Matrix Manager.  Limited
     studies, e.g., literature surveys, are conducted on selected topics to determine the available
     state of knowledge. Workshops may be held to obtain a better understanding and analysis
     of that information. Based on these inputs, a decision can be made as to whether additional
     information is needed and, if so, what specific research should be conducted. Selected
     national and international meetings on indoor air quality are sponsored to facilitate the
     availability of current knowledge in this area. Technical reports of results from the Indoor
     Air Research Program are published in a special Indoor Air technical report series.

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D.   Milestones:
     Program Management:

     •     Support of WHO meeting: Indoor Combustion Products

     •     Report on the EPA Indoor Air Research

     •     Sponsorship of international meeting: Indoor Air '90

     •     Support of NATO-CCMS Indoor Air Work Group

£.   Project Contact:

     Michael A. Berry  (919) 541-4172
                     (FTS) 629-4172
F.   Resources:


     FY90
1.0
         S&E
S58.2K
 R&D

$75K
TOTAL

S133.2K
                                                     11/89

                                                      6/90

                                                      7/90

                                                      7/90

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INDOOR AIR HEALTH IMPACT AND RISK ASSESSMENT

FTEs
S&E
R&D
TOTAL
FY87
1.0
0.0
153.0
153.0
EXSS
2.0
120.0
269.0
389.0
FY89
2.0
120.0
227.0
347.0
EX2Q
2.0
116.2
163.6
279.8
FY91
1.0
205.0
425.0
630.0
   Benefits to be Derived:

   The ultimate goals in addressing indoor air quality problems are to characterize and understand
   the risks to human health that indoor pollutants pose and to reduce those risks by reducing
   exposures. The characterization of risk from indoor pollutants varies in relation to understanding
   their sources, exposures, and dose-response information.  The most well known indoor air
   pollutants originate from a variety of sources. These sources generate wide ranges of pollutant
   concentrations over time.  Actual human exposure to many of these  pollutants is not well
   understood.  Exposure and risk assessment is one of the indoor air research community's most
   important research activities.
   Historical Perspectives:

   One of  the biggest deficiencies highlighted in EPA's preliminary assessment of indoor
   environments hi  1986 was the inability of the scientific community to properly assess human
   risk from indoor air pollution. This shortcoming is the result of limited data on human exposure
   to the many different pollutants found indoors and the inability to distinguish among multiple
   health endpoints. Consequently, one of the highest research objectives has been to develop data
   and information with which to better characterize exposure and health effects to determine risk.

   A risk assessment methodology has been developed that utilizes data collected in indoor studies.
   The framework follows the traditional risk model chain: sources, transport and fate, exposure,
   dose, and effect. The assessment methodology has been  used to evaluate the strengths and
   weaknesses of published risk assessments for indoor air and has been used  to help evaluate
   exposure to benzene. The risk assessment methodology will be expanded to assess noncancer
   effects and to use more advanced exposure assessment models.

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Fiscal Year 1989:

In the area of exposure assessment and risk characterization, activities were extended into a more
focused and realistic characterization of national indoor air quality.  The risk/health impact
characterization framework was enhanced using personal computer software and more accurate
exposure estimates.  The effects of biological contaminants continues to be evaluated to the
greatest extent possible using available medical information.  During FY89,  a survey of the
research needs of state and local governments was conducted. The results will be used to plan
research and assistance to states  and local governments for future years.  EPA published its
bibliographic data base that contains over 4,000 indoor air related reference citations.
Fiscal Year 1990:

Common indoor air quality scenarios will be evaluated in an effort to develop a method by which
to assess the noncancer or nonfatal effects of indoor exposure.   Examples include predicted
human response to new carpets and asthmatic response to N02 and biological contaminants. The
most common indoor air carcinogens will be identified and assessed using EPA's formal risk
assessment process.
Fiscal Year 1991:

The general development of risk methodology procedures and the performing of assessments for
major indoor air pollution scenarios will be continued.  The base program will provide for
improved exposure assessment models.  A risk assessment of child exposure to biocontaminants
in schools under various ventilation conditions will be conducted.  Scenarios will be conducted
using the risk assessment methodology developed in FY88-90.  Risk of upper respiratory disease
will be emphasized.  Computer simulation models will be developed to assess human exposure
indoors.  The simulations will be based  upon use of CIS software and illustrate air quality
resulting from pollutant mixtures and typical ventilation conditions.

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PROJECT 2:  RISK   CHARACTERIZATION  METHODOLOGY   AND   RISK
A.   Objective:

     Continue development of a risk characterization methodology to consistently assess different
     indoor air pollution scenarios; apply this methodology to assess the risks of specific indoor
     air pollutants, including environmental tobacco smoke and kerosene heater emissions.

B.   Background:

     For EPA to  determine the potential health risks presented by indoor air pollution,
     methodology is needed to characterize the risk presented by each pollutant. Although there
     are many gaps in the  information  regarding the risks due to  such pollutants,  much
     information is available that can be assessed. Based on this risk determination, the general
     public can be advised as to what considerations may be necessary to minimize that risk.
     This information will also be used to establish research priorities  for effective mitigation
     measures.

C.   Approach:

     Apply the newly developed risk characterization methodology to specific pollutants and. risk
     factors, and modify the methodology as appropriate.  Results of risk determinations for
     each pollutant evaluated will be published.  Evaluate common indoor air quality scenarios
     to develop a method to assess noncancer or nonfatal effects of indoor exposures. Examples
     include predicted  human response to new carpets and asthmatic response to NO2 and
     biological contaminants. The most common indoor air carcinogens will be identified and
     assessed using EPA's formal risk assessment process.
D.   Milestones:
           Issue preliminary assessment of biocontaminants

           Apply risk characterization methodology to the assessment of
           formaldehyde and 1,3-butadiene

           Development of a profile of time activity patterns for indoor
           air exposure in coordination with TEAM studies

           Development of an integrated risk/health assessment data base

           Development of a draft risk characterization methodology for
           noncancer endpoints
2/90

5/90


8/90


9/90

9/90

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E.   Project Contact:

     Michael A. Berry


F.   Resources:


     FY90
      (919) 541-4172
      (FTS) 629-4172
FTE     S&E      JR&D

1.5     $87. IK     $155K
 TOTAL

$242. IK

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PROJECTS:  PUBLIC ATION OF THE INDOOR AIR REFERENCE BIBLIOGRAPHY

A.   Objective:

     Publish the Indoor Air Pollution Reference Bibliography, which includes citations on all
     aspects of indoor air pollution.  This information will assist researchers in identifying
     available information dealing with a specific area in indoor air pollution.

B.   Background:

     The Indoor Air Pollution Reference Bibliography is an extensive compilation of reference
     materials on indoor air pollution. Because this is an area of rapidly expanding research,
     it is necessary to continually search and retrieve publications from the scientific literature
     to maintain a current data base.

C.   Approach:

     As new information is retrieved  and evaluated, it is incorporated into the reference data
     base, which contains over 4,000 references. The citations are indexed by key words so that
     published articles can be identified in specific areas.
D.   Milestones:

     Publication of Indoor Air Reference Bibliography

E.   Project Contact:

     Norman Childs
       (919) 541-2229
       (FTS) 629-2229
F.   Resources:
     FY90
                                                          8/90
0.5
S&E
$29. IK
R&D
$8.6K
TOTAL
S37.7K

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           INDOOR AIR BUILDING  STUDIES AND
                    METHODS DEVELOPMENT

FTEs
S&E
R&D
TOTAL
FYJ2
3.0
210.0
767.0
977.0
FY88
3.0
174.0
533.0
707.0
FY89
3.0
181.5
616.0
797.5
FY90
3.0
226.1
564.4
790.5
FY91
3.0
299.4
13135
1612.9
Benefits to be Derived:

Building studies will identify and characterize indoor problem areas, collect data bases needed
to validate measurement methods and models, and provide empirical data for risk and health
impact assessments. As the public becomes more knowledgeable of indoor air pollution, more
complaints will be voiced concerning problems in residences and commercial buildings. In many
cases a building study effort is the only way to determine the magnitude of the problem and to
identify potential corrective actions. Special measurement studies in "Sick Buildings" are needed
that define standardized approaches to SBS investigations with the highest probability of success
at minimum cost.  Field testing of indoor measurement methods is the only way to determine
their practicality and unobtrusiveness.

Research will continue in the development of improved measurement methods and supporting
reference materials, collection of empirical data in special microenvironmental field studies, and
the development and validation of predictive models. These measurement-related activities must
be integrated  to determine the role that  selected indoor microenvironments play in total air
exposure.  The development of measurement methods for indoor environments is a critical  first
step in being able to quantify distributions of concentration and exposure.
Historical Perspective:

Considerable progress has been made in recent years in the development of practical detectors
for indoor contaminants. Passive samplers and personal monitoring devices have been developed
for volatile organic compounds, formaldehyde, and nitrogen dioxide.  An electrochemical NO2
personal exposure monitor that measures in real time has also been developed that can measure
pollutant levels down to 10 parts per billion.  These samplers are important to the indoor air
program because they can be worn on clothing and can be used to indicate areas with the highest
pollutant concentrations. For example, changes in pollutant levels can be measured as the wearer
                                        10

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moves in and out of a room that has a combustion appliance in use.  Measurements can also be
gathered from within a car, parking garage, or dry cleaning establishment.  Exposures can be
examined  during  personal activities, such as  cleaning,  stripping furniture,  or  after new
furnishings have been installed in a home or office. These samplers are used to more accurately
predict exposure scenarios where high pollutant levels may be present.

Studies have been conducted in the development of quiet, unobtrusive sampling methods and
characterization techniques for semivolatile compounds (SVOCs).  Laboratory tests have been
completed on an initial prototype, and construction of two more samplers and evaluation of their
performances in occupied homes is planned. SVOCs are products of combustion, and although
the health effects they cause are not well understood, some are  suspected to cause cancer
(polycyclic aromatic hydrocarbons) and neurotoxic effects. A new method for sampling nicotine
and polycyclic aromatic hydrocarbons together was developed and evaluated in homes.

A compendium of measurement methods  has been compiled to provide Standard Operating
Procedures and technical assistance.  This effort will help standardize the format for emerging
measurement technology for use  in homes and offices.   Monitoring methods have been
recommended for VOCs  and nicotine.

EPA haJTdeveloped the necessary skills to begin evaluating problem buildings. The recent study
of the Library of Congress is an example. The first phase of this study will gain some measure
of SBS symptoms and  exposure variables through the use of questionnaires, and should help to
refine the use of questionnaires in future building investigations.

EPA researchers have also responded to  the immediate  needs  of their own  agency  in  the
investigation of complaints of EPA  headquarters in Washington,  D.C.  Extensive air samples
were taken, materials (carpets) were evaluated, and a report on sampling results was submitted
to EPA management. Based on the experience gained in building investigations and the success
achieved in developing measurement devices, EPA research is now ready to expand activities in
the direction of more formal field studies and investigations.
Fiscal Year 1989:

Research continued in the development of measurement methods and modeling activities. By the
end of the fiscal year EPA's four year collaboration with NIST will deliver a user-friendly model
(CONTAM) for the evaluation of large complex office buildings.  EPA is also making its own
10-chamber indoor air model available to the public. .A compendium of 10 sampling methods
will be published by EPA at the end of the fiscal year. EPA continued to make headway in the
development of passive monitors for N02 and VOCs. Research continued in the development
of active samplers for SVOCs.
                                         11

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Fiscal Year 1990:

The Indoor Air Monitoring and Building Studies Program emphasizes monitoring and analytical
methods development, building diagnostic and remediation methods,  and technology transfer.
Monitoring and analytical methods development research  will include the development and
evaluation  of personal  and  microenvironmental  monitors for SVOCs and polar organic
compounds; and  the development of quality assurance standards for compounds routinely
measured indoors (e.g., nicotine and semivolatile compounds).  Research will also include final
evaluation of aerosol and gas phase emissions from kerosene heaters and analysis of soluble and
insoluble compounds in  humidifier aerosols.  Research in building diagnostic  and remediation
methods will include the evaluation of indoor air quality data from the Library  of Congress and
EPA/Waterside Mall buildings and the development and refinement of procedures to evaluate
large  building exposure assessment and indoor air quality problems.  Technology transfer
activities will  include the publication of the compendium of indoor  air quality measurement
methods.
Fiscal Year 1991:

Monitoring and analytical methods research  will focus on instruments for SVOCs  and on
screening questionnaires and instruments for large building diagnostic studies.  Characterization
research will include investigations of complaints in commerqial buildings. Research in building
diagnostic and  remediation approaches to building diagnostic investigation  and analysis will
continue. Technology transfer of indoor air quality measurement methods will continue through
publication of additional volumes of the compendium of indoor air quality methods.

In FY91, EPA's capability to study buildings will be greatly expanded.  The building  study
program will apply diagnostic procedures developed by the research program and will integrate
the monitoring and health resources of the Agency in a coordinated effort to explain and evaluate
environmental conditions and the status of health found indoors, especially in large buildings.
Studies will be conducted that evaluate both  normal  and complaint buildings so as to better
predict when and the type of health problems that will likely occur in the presence of a particular
indoor air quality scenario.   Studies will also begin  that evaluate  the  productivity of office
workers exposed to unhealthy indoor  air.  Efforts will begin with  other Federal agencies to
develop standardized methods for measuring biological contaminants. Procedures to investigate
the contribution of HVAC equipment to indoor biological contaminant levels will be developed.

A formalized body of knowledge related to building science will be developed.  The following
will  be initiated:  investigation of potential sources  and ventilation problems (preferably in
Federally  owned or  leased office  building(s)  with  occupant complaints);  development of
corrective  actions;  implementation of corrective actions  and  evaluation  of results; and
establishment of guidelines for problem building evaluations and corrective actions.
                                          12

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PROJECT 4:  COMPUTER ASSISTED SOFTWARE FOR UPGRADED NIST INDOOR
              DISPERSION/VENTILATION MODEL

A.   Objective:

     To upgrade the existing EPA/NIST dispersion/ventilation model with computer assisted
     software facilitating its use by building designers, contractors, and scientists.  A major
     priority of the indoor air program is the development and validation of a sophisticated air
     transport model capable of describing the growth, equilibrium,  and decay of indoor air
     pollutants under multizoned building conditions.  The final computer-assisted model must
     be user-friendly  for potential users  having  diversified technical backgrounds.   Once
     developed, available indoor data will be used to evaluate the user-friendly model.
                                                    i
B.   Background:

     EPA and DOE entered into an IAG with NIST to develop and validate a general framework
     model that predicts indoor air quality under multizone building conditions.  The model first
     treats each zone and constituent individually and secondly evaluates zones and pollutants
     as an integrated system under single HVAC system environments.  FY88 research extended
     the improved model's capabilities facilitating the characterization of indoor air quality
     under conditions  where multiple HVAC systems were being employed.  Recent efforts
     enhanced the model's capabilities and promotes pollutant concentration projections under
     conditions other than well mixed. Although technically sound, the existing model is not
     readily employed by indoor air investigators.  A work assignment was issued during FY89
     to develop computer-assisted software to render  the model user friendly.  Once this is
     completed, available indoor data will be used to validate the model.

C.   Approach:

     Computer assisted software is being developed by NIST to facilitate the model's use by all
     indoor air investigators, regardless of technical background or modeling experience. Once
     they are received, available indoor environmental data will be used to test the useability of
     the model.  When it is validated, flexible disk copies with associated instructions of the
     computer assisted model will be made available to the public to assist contractors, builders,
     managers, and scientific personnel to better  design and develop environmentally office
     complexes.
D.   Milestones:
           Initiation of task with NIST

           Delivery of computer assisted software with instruction manual
6/89

6/90
                                         13

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     •    Test of model using available indoor air data from
          large building studies

     »    Preparation of final report of model

E.   Project Contact:
                                                        7/90
                                                        9/90
     John Irwin
F. Resources:
     FY90!
       (919) 541-1323
       (FTS) 629-1323
0.3
                               S&E
$22. IK
R&D

SOK
TOTAL

$22. IK
                                        14

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PROJECTS:  QUALITY ASSURANCE STANDARDS

A.   Objectives:

           To develop analytical QA standards to support specific needs of the Indoor Air
     Program. To review past and planned Indoor Air Program monitoring studies and establish
     lists of targeted indoor air contaminants and concentrations.  Initial emphasis will be placed
     on the development of standards for vapor- and particle-phased nicotine as well as other
     semivolatile compounds collected on XAD-2, XAD-4, or PUF absorbents.

B.   Background:

     Quality assurance reference standards are essential components of all monitoring and
     analytical studies. Various reference standards have been developed for environmental
     contaminants commonly observed at high  concentrations in ambient air.   Indoor air
     pollutant  concentrations are significantly lower than those experienced in ambient air.
     Extensive research has been conducted to  develop QA standards for volatile  organic
     compounds using either the solid absorbent or evacuated canister monitoring method.
     Although QA standards for individual  chemical  species are  normally commercially
     available, composite  QA  samples containing known concentrations  of multiple target
     compounds mimicking environmental samples are not readily available.  In addition, QA
     reference standards are not readily available for newly developed sampling and analytical
     techniques.  Without external quality assurance data, routine indoor air investigation results
     may not be relatable and are considered marginal.

C.   Approach:

     Research conducted during FY90 will continue to emphasize the FY89 progress. Primary
     emphasis  will be placed on  developing nicotine  and PUF/XAD-2 semivolatile QA
     standards. Developed reference materials will be  validated and made readily available to
     support monitoring programs.   Standards covering multiple concentration ranges will be
     prepared  and  evaluated  to  determine  optimum  analytical precision  and  accuracy.
     Compound stability, species and/or matrix interferences, and shipping/storage effects will
     also be evaluated.
D.   Milestones:

     *     Evaluation of stability of nicotine standards

     *     Evaluation of stability of PUF/XAD standards

     •     Report on evaluation of effect of storage on standards
11/89

12/89

 6/90
                                         15

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£.  Project Contact:

    Berne Bennett


F. Resources:



    FY90
(919) 541-2366
(FTS) 629-2366
FTE     S&E       R&D

0.2     $15K       $30K
                         $45K
           16

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PROJECT 6:  COMPENDIUM OF INDOOR AIR QUALITY METHODS

A.   Objective:

     To compile the most commonly employed indoor air quality monitoring and analysis
     methods into a standard-format compendium for distribution to participating federal, state,
     local, and private agencies.   The manual consists of monitoring procedures, analytical
     procedures, and a technical assistance document.

B.   Background:

     Previous attempts to standardize indoor air quality methodologies have been fragmented,
     inconsistent in format and/or technical information, or incomplete. In addition, indoor air
     technology is rapidly emerging,  with  many  state-of-the-art monitoring  and analytical
     techniques being not fully evaluated and/or documented. Technical  assistance documents
     assisting investigators in selecting when and how to employ indoor air procedures are not
     readily available. As a result, indoor air quality data are not consistent among studies. An
     EPA sponsored compendium is needed that compiles the most commonly used monitoring
     and analysis methods.  Once the compendium  is peer-reviewed,  the universal format
     procedures will be distributed to the public in a loose-leaf binder format that will allow for
     easy updating. Methods contained in the compendium are for: VOCs; nicotine; CO and
     CO2; air exchange rate; NO2; formaldehyde and other aldehydes; benzo(a)pyrene and other
     PAH's; organochlorine pesticides; annular denuder system; and participate matter.

C.   Approach:

     Obtain indoor  air methodologies and  associated procedures  employed by the  user
     community. Consolidate the procedures, conduct a formal peer-review, produce initial and
     revised editions in a common format, prepare a companion technical assistance document,
     and distribute the compendium to the indoor air investigators. An  abbreviated technical
     version will be developed for reference by field and laboratory personnel.  All documents
     would be assembled to facilitate copy control and revision.

D.   Milestones:
     •     Completion of peer review

     •     Draft method for biologicals

     •     Draft technical assistance document
10/89

11/89

 1/90
                                         17

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     •    Draft abbreviated Compendium

     »    Publication of Compendium

     •    Publication of TAD

     •    Publication of abbreviated Compendium

     •    Initiation of peer review of Compendium

£.   Project Contact:

     Frank McElroy
      (919) 541-2622
      (FTS) 629-2622
F. Resources:


     FY90
0.5
 S&E

$38K
 R&D

$45K
                                                      3/90

                                                      4/90

                                                      8/90

                                                      9/90

                                                      9/90
TOTAL

 $83K
                                      18

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PROJECT?:  MONITORING METHODS DEVELOPMENT

A.   Objectives:

     Develop and evaluate integrated microenvironmental monitors simultaneously collecting
     particles, VOCs, SVOCs,  nicotine, and selected continuous parameters.  Develop and
     evaluate low-cost passive exposure monitors for use as screening and survey tools for
     selected parameters and personal exposure monitors for selected parameters.

B.   Background:

     Characterizing indoor  environments  and  assessing personal exposures requires  the
     simultaneous collection  of multiple pollutants over extended time periods. A multiplicity
     of screening,  microenvironmental, and personal monitoring  methods are currently being
     employed by indoor air investigators. Each technique features technical strengths but may
     not produce relatable environmental data.  Low cost and unobtrusive screening techniques
     are limited to single or dual pollutants and are increased  experimental and analytical
     uncertainties.  However, when employed correctly, personal monitor data provides more
     representative individual exposure  data.   Microenvironmental  monitors provide large
     volume samples  supporting  detailed chemical  analysis.    The data  represent an
     environmental zone containing multiple sources and are influenced by many personal
     activities.  When these monitors are used in combination with other monitors,  the source
     requirements, noise, and obtrusiveness may result,in altered participant  lifestyles and
     activities.  Improved integrated monitoring techniques must be developed to better evaluate
     the overall impact of outdoor and indoor sources on the indoor environment and assess
     personal exposures.

C.   Approach:

     New and improved passive, personal, and microenvironmental monitoring techniques will
     be independently designed, developed, and evaluated.   Design parameter considerations
     include species,  analytical requirements,  sample  media,  quality  assurance, resource
     requirements, and obtrusiveness.  Additional field evaluation of previously developed low
     cost  passive  monitors  for N02, VOCs,  and SVOCs will  be conducted  to include
     side-by-side comparisons with certified methodologies.  Prototype PEM particle, nicotine,
     and SVOC samplers will be designed,  miniaturized, developed, and evaluated.  Prototype
     PEMs  simultaneously collecting particles, nicotine,  CO, and NO2 will also be developed
     and evaluated. The newly developed  20 L/min sampler will be extensively tested under
     field conditions.  A low flow-rate compound annular denuder will be designed and tested
     to evaluate the phase distribution of SVOCs. Integrated microenvironmental monitors that
     simultaneously collect particles, SVOCs, VOCs, RH, T, and criteria pollutants will be
     designed, developed, and field tested.
                                          19

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D.   Milestones:
           Comparison of collection and analysis techniques for organic
           compounds

           Development and testing of integrated microenvironmental
           sampler

           Journal article - "Effect of Temperature on NO2 PSDs"

           Evaluation of newly developed procedures to collect and quantify
           polar organic compounds

           Design and development of annular denuder for 20 L/min SVOC
           sampler

           Extension of PSD to other pollutants such as formaldehyde and
           nicotine

           Development and testing of integrated personal sampler

           Field testing of 20 L/min SVOC sampler
                                                        12/89


                                                        12/89


                                                        12/89

                                                         3/90


                                                         3/90


                                                         3/90


                                                         4/90

                                                         4/90
E.   Project Contacts:

     Ross Highsmith
     (Microenvironmental)

     Jim Mulik
     (PSD)

F.   Resources:
     FY90
0.5
       (919) 541-7828
       (FTS) 629-7828

       (919) 541-3067
       (FTS) 629-3067
 S&E

$38K
$55K
TOTAL

 $93K
                                        20

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PROJECTS: ANALYTICAL METHODS DEVELOPMENT

A.   Objectives:

     Develop and evaluate  analytical procedures for targeted polar and  nonpolar  organic
     compounds and personal sampling devices (PSDs). Determine precision, accuracy, species
     stability, interferences, and  collection  efficiencies of  commercially  available  solid
     absorbents for organic compound classes.

B.   Background:

     Indoor  air investigators  must be assisted  with the technical expertise to determine
     environmental parameters, collection methods,  and  analytical techniques employed  in
     indoor environmental investigations.  Past indoor air research studies primarily used solid
     absorbents for organic  compound collection based on availability and costs.  Evacuated
     canister VOC techniques are proposed.  Once the sample is collected, the investigator must
     determine the appropriate analytical technique. Limited technical support documentation
     is  available to assist investigators in the decision process for selecting collection and
     analysis  mechanisms.    Analytical  methodologies  for  ambient  and  source  sample
     characterization are not always directly applicable to indoor air sample analysis  as these
     procedures may not provide the sensitivity or selectivity required.

     Polar organics and marker compounds for numerous suspected carcinogens are not routinely
     collected, extracted, or analyzed from indoor samples, regardless of collection media.
     Physical and chemical characteristics of polar organics require extensive, and sometimes
     species-specific, sample preparation and analytical techniques.  Technology changes result
     in  the formation of newly identified indoor contaminants, e.g., 4-phenylcyclohexene, for
     which  no standardized analytical procedure exist.   Collection protocols also impact
     analytical results.  Bulk samples support detailed  chemical analyses not feasible from low
     flow rate PEM/PSD sample analyses.  Improved analytical  techniques  to identify and
     quantitate chemical species, both large- and small-volume samples, must be developed.
     Research must be  conducted  to document the strengths  and  weaknesses of the use  of
     commercially available  organic sampling  media.

C.   Approach:

     Organic compounds (VOCs, SVOCs, PAHs, etc.) in indoor air samples will be chemically
     characterized and quantified to determine the stabilities of the species, analytical precision
     and accuracy, and potential interferences.  Polar and nonpolar  organic compounds will be
     tested with  improved procedures developed to  collect, separate, detect, confirm, and
     quantitate specific species. Research will determine polar VOC degradation products and
     their effects on the analytical results.  Marker compounds will be identified, and the target
     compound list will be updated. Enhanced PSD analytical techniques will be developed and
                                          21

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     compared to standard  analytical techniques thus increasing the overall usefulness of
     lowflow-rate devices in indoor monitoring programs. Analytical methods will be developed
     and improved for the identification and quantitation of both known and hitherto unknown
     compounds. Research will improve technical understanding of the strengths and limitations
     of commercially available collection media and standard laboratory analytical methods for
     routine organic compound analysis.
D.   Milestones:
           Report - "Development of real-time formaldehyde monitors"

           Report - "PSD versus canister comparison for VOC
           collection and analysis"

           Evaluation of newly developed procedures to collect and
           quantify polar organic compounds

           Paper - "Evaluation of Cl-ion trap mass spectrometer for
           the analysis of ambient polar volatile organic compounds"
                                                        12/89

                                                        12/89


                                                        4/90


                                                        10/90
E.   Project Contacts:

     Nancy Wilson
     Jim Mulik
     (PSDs)

F.   Resources:
     FY90
(919) 541-4723
(FTS) 629-4723

(919) 541-3067
(FTS) 629-3067
        S&E

        $38K
0.5
 R&D

$80K
TOTAL

S118K
                                         22

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PROJECT 9: LARGE BUILDING STUDIES

A.   Objectives:

     Support the Library of Congress and EPA Headquarters buildings studies and Regional
     Office and State agencies in indoor air evaluations.  Develop large building diagnostic
     protocols to include the characterization of physical, chemical, and personal parameters.
     Test and evaluate IAQ program monitoring and analytical procedures to evaluate indoor air
     quality in residences and large office buildings.  Develop revised procedures and technical
     expertise to evaluate "SBS" or high complaint buildings. Evaluate microenvironmental and
     personal source monitoring protocols that relate measurement/analysis data  to personal
     exposure and risk assessments.

B.   Background:                                                                 !

     Most indoor air investigations are limited in scope as  a result of the exhaustive resource
     requirements needed to simultaneously evaluate a facility's physical parameters and multiple
     environmental  contaminants,  and relate  these to  personal exposures and  symptoms.
     Preliminary surveys or easily identified sources have been used as the study design  basis
     while monitoring and analytical protocols are aligned to support these hypotheses. These
     approaches are successful in environments with significantly known single or dual sources.
     Study results from  more complex source and area conditions have not been as definitive.
     Modern office complexes are impacted by  a  multiplicity of environmental, variables.
     Individual as well as synergistic effects increase the difficulty in characterizing a facility's
     indoor air quality.  SBS investigations require comprehensive monitoring,  analytical, and
     survey programs to fully characterize and quantitate the indoor environment and correlate
     these findings to exposures and risks. Additional research is needed to ensure that future
     indoor investigations provide the necessary data to support exposure and risk assessments.

     The Library of Congress (LOG) and EPA Headquarters buildings have historically reported
     classical SBS symptoms. Initial investigations were limited in resources and did not include
     the necessary personal and environmental data required to fully characterize the indoor
     environments,  identify or quantify pollutants, or eliminate the responsible source(s).  A
     multiagency task force was organized to characterize the LOG Madison Building and  EPA
     facilities, to assess  exposures as well as risks and to develop identified source mitigation
     strategies.  The resulting procedures will be  validated in subsequent high complaint
     facilities to better define  the indoor air quality data required  to identify, quantify, and
     mitigate "SBS" symptoms.

C.   Approach:

     A comprehensive  monitoring study was conducted  at the LOC Madison and  EPA
     Headquarters buildings to characterize the indoor environments, correlate employee health
                                          23

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     related symptoms to environmental parameters, and develop strategies to improve the
     indoor air.  Particles,  volatile organics, semivolatile organics, and routine continuous
     measurements were conducted daily at multiple locations over a one week period.  A
     multipurpose questionnaire was developed and administered to all fulltime employees to
     comprehensively assess personal and temporal parameters. The results are being analyzed
     to identify the parameters responsible for the SBS  implications.  Follow-up studies in
     additional high complaint office complexes will be conducted to support regional office and
     state agencies and to validate the indoor air quality protocols and LOG results.
D.   Milestones:
           Draft report of LOG results

           Draft report of EPA results

           Final report of LOG results

           Final report of EPA results

           Draft report of LOG exposure assessment

           Draft report of EPA exposure assessment

           Draft report assessing LOG/EPA buildings
                                                11/89

                                                12/89

                                                 1/90

                                                 2/90

                                                 6/90

                                                 8/90

                                                 9/90
£.   Project Contact:

     Ross Highsmith


F.   Resources:




     FY90
                      1.0
                             (919) 541-7828
                             (FTS) 629-7828
 S&E        R&D

$75K       S354.4K
 TOTAL

S429.4K
                                         24

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                INDOOR AIR HEALTH EFFECTS

FTEs
S&E
R&D
TOTAL
FY87
1.7
100.0
550.0
650.0
FY88
1.0
100.0
625.0
725.0
FY89
1.0
61.1
960.0
1021.1
FY90
1.0
60.2
949.1
1009.3
FY91
5.0
310.0
841.6
1151.6
Benefits to be Derived:                           ;.'

Health research related to indoor air quality is designed to explain how, why, and the extent to
which humans respond to the mixture of compounds found in microenvironments; to assess by
way of biomarkers the extent to which children are exposed and receive into their bodies harmful
and unwanted products of tobacco smoke; and to predict through animal testing the  general
irritation, pulmonary, and neurobehavior response in humans from exposure to emissions from
a variety of sources found in indoor environments.
Historical Perspective:

During FY87, 88, and 89, the Indoor Air Health Research Program built  and tested its
capabilities to measure human response to volatile organic compounds often found in indoor
environments and associated with building complaints and "sick-building syndrome."  The work
of Molhave has been replicated by EPA's research program.  During FY88 and 89, headway was
made in developing an ETS exposure model for children using the biomarker metabolite cotinine.
When completed,  this model will allow researchers to evaluate the extent to  which control
strategies for ETS are effective and the extent to which children are exposed.   During FY89,
work began to integrate animal testing as a part of the indoor sources testing program. Animal
testing has previously not been a part of the indoor health research program.
Fiscal Year 1989:

Human response to VOC mixtures was studied to replicate the finding of a Danish study
(Molhave,  1984) and to evaluate behavioral and  sensory irritant effects.  The role of the
olfactory nerve and trigeminal nerve was examined in relation to human behavior.  Research
evaluated the use of cotinine as a biological marker of exposure to nicotine for ETS.  Kerosene
heaters were tested to evaluate health consequences resulting from concentrations of SO2, SO4,
NO2, H2S04, and a variety of VOCs.
                                        25

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fiscal Year 1990:

Hie  following areas will be emphasized:  effects of VOC mixtures on neurobehavioral and
physiologic effects in humans, and the establishment of an animal inhalation exposure facility to
assist in evaluating VOCs. For VOCs and chemical mixtures, a more realistic and sensitive line
of research is necessary. The focus of the research is the hypersensitivity, neurotoxicity, and the
annoying properties of chemical mixtures.  In ETS research, emphasis will be on determining the
distribution of constituents in the paniculate and vapor phases of ETS  and identifying and
evaluating marker compounds for these two phases of ETS.
Fiscal Year 1991:

Efforts will continue to assess human response to mixtures.  Biomarker research will continue
to examine ways cotinine can be used to estimate exposure to ETS.  Research efforts in FY91
will be expanded to emphasize the noncancer health effects using animal studies.  Assessments
of the genotoxicity of emissions  from various indoor combustion appliances and associated
mitigation strategies will be completed. Studies will better characterize human response to the
complex emission components of indoor sources.  The work  will help to identify potential
sources of health hazard for more detailed investigation in FY92 - FY95.
                                          26

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PROJECT 10:  NEUROBEHAVIORAL,  RESPIRATORY,  AND SENSORY IRRITANT
               EFFECTS OF COMPLEX VOC MIXTURES IN HUMANS

A.   Objective:

     Perform studies of controlled human exposures to complex VOC mixtures,  showing
     elements of the sick building syndrome (SBS).

B.   Background:

     Sick building syndrome (SBS) results in considerable lost work time and worker discomfort
     each year.  Whether the perceived effects of exposure to indoor air pollutants constitute real
     or imaginary hazards to human health is an important and controversial question.  Since
     VOCs  are widely  used  in construction  and industry  as solvents,  plasticizers, and
     preservatives, the confirmation (or  discontinuation)  of effects ultimately will  have
     substantial impact on this class of indoor air pollutants.  Work performed last year
     produced somewhat different results from the Molhave study, but validated the adverse
     nature of VOC exposures on indoor concentrations in healthy young adult males.

C.   Approach:

     In the study, normal healthy adults or,  if possible, hypersensitive adults will be exposed to
     a complex mixture, of volatile organic  compounds as similar as possible to the most often
     found mixture, substituting only for chemicals now known to be carcinogenic. Behavioral,
     respiratory tract, and sensory irritant subjective rating measures will be obtained from
     subjects using a repeated measures design in which each subject will complete control and
     exposure sessions at one week intervals.  Studies will explore effects of a VOC mixture
     characteristic of American buildings, VOC exposure in SBS responder or other susceptible
     populations (if adequate numbers of subjects can be recruited), and the role of olfactory and
     trigeminal sensitivity.   Nasal lavage specimens  will be  analyzed for inflammatory
     indicators. A threshold study to determine the minimal effect concentration for observed
     behavioral or discomfort effects will be examined and perhaps extended  to field studies.
D.   Milestones:

     •     Development of a dose-response model for discomfort

     •     Assessment of responsibility of sensitive groups to inhaled VOCs

E.   Project Contacts:
                                                  5/90

                                                  11/90
     George Goldstein
     Dave Otto
(919) 966-6200
(919) 966-6226
                                        27

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F.  Resources:
                            S&E       R&D
    FY90
1.0
S60.2K     $475.2K     S535.4K
                                     28

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PROJECT 11:  BIOLOGICAL MARKERS FOR ENVIRONMENTAL TOBACCO SMOKE
               (ETS) EXPOSURE AND DOSIMETRY IN CHILDREN AND ADULTS

A.   Objectives:

     Quantitate ETS exposure using bioassay and biomarker methods.

     Evaluate current biological markers (e.g. nicotine/cotinine) for their use in effectively
     assessing the exposure and dosimetry of ETS by:  determining if urine cotinine levels in
     infants and young children are a quantitative measure of exposure to ETS; determining the
     elimination half-life of urinary cotinine as a function of age, sex, or other parameters
     affecting metabolism  in children; quantitating nicotine  intake from ETS and validating
     current biomarkers (nicotine and its metabolites,  cotinine and 3-OH cotinine) by using
     deuterium-labeled nicotine in clinical ETS exposure studies; and determining the influence
     of exposure variables on ETS intake.  Develop, evaluate, and apply DNA adducts and other
     molecular exposure dosimetry methods to human studies.

B.   Background:

     Human  studies  show an  increased  risk  of adverse health effects (e.g., cancer and
     respiratory effects), due to exposure to ETS. Quantitation of these risks is dependent  on
     obtaining improved data on ETS exposure, intake, and dosimetry. Several national reports
     on ETS have highlighted the high priority need for  research on biological markers for ETS
     exposure and dosimetry.

C.   Approach:

     A  multidisciplinary approach to these ETS  exposure-dosimetry studies  will include
     evaluation of biological and chemical markers of ETS in  controlled chamber studies,
     homes, and in other microenvironments. Targeted  pilot field studies are being undertaken
     colkboratively by  EPA and UNC investigators at  the Frank Porter Graham (FPG) Child
     Development Center.  There are forty children enrolled in the Center from ages 3 months
     to 5 years. Approximately half of the children's parents smoke cigarettes.  The homes of
     selected children enrolled in the (FPG) Center for Child Development (operated by UNC
     as a research day care center) are monitored for a series of pollutants including nicotine and
     mutagenicity. Body fluids of these  preschool children both exposed and nonexposed to
     ETS will be used in biological marker studies.

     Adults and young children from homes where tobacco smoke is present will be exposed to
     known concentrations of ETS  in an  environmentally controlled chamber.  Urine will  be
     collected from subjects, prior to exposure, up to several days postexposure. Urine cotinine
     excretion rates will be determined and correlated with air nicotine exposure. Validation
     studies will be conducted in adults using dueterated nicotine to quantitate the relationship
                                         29

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     between exposure uptake and elimination. The dose of nicotine will be varied by changing
     the number of cigarettes smoked during the exposure to give a dose response.   The
     excretion of cotinine will be correlated with the dose of nicotine as well as age, sex, and
     race in the infant/child  population.   This information is critical because  it will allow
     estimation of  prior exposure, with a  high  degree of certainty,  rather than rely on
     questionnaire data.  This study was undertaken to determine the exposure dose of nicotine,
     the peak level of urinary cotinine, the time to peak levels of cotinine, and the elimination
     half-life of urinary cotinine when children are exposed to a controlled amount of ETS.

     The  use of DNA adducts as determined by 32P-postlabeling is being developed as a
     molecular biomarker of exposure to tobacco smoke.  The initial approach has involved the
     development of this method in vivo and in vitro exposures to complex mixtures. Lung cells
     from bronchioalveolar lavage of humans in clinical studies have provided evidence that
     smoking adducts are detectable.
D.   Milestones:
           Report on monitoring human exposure to ETS in homes and various
           microenvironments using biomarkers

           Assessment of preschool children's exposure to ETS using nicotine,
           mutagenicity, and cotinine

           Establishment of relationship between personal exposure to
           nicotine and other pollutants (e.g., mutagens, RSP) and cotinine

           Determination of elimination half-life of cotinine in young
           children exposed to different dose levels of ETS

           Evaluation of ETS dosimetry in humans using DNA adducts
 4/90
 1/91
10/91
 5/92
11/93
                                          30

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                                                                                         I
£.   Project Contacts:

     Joellen Lewtas


     George Goldstein

F.   Resources:



     FY90
      (919) 541-3849
      (FTS) 629-3849

      (919) 966-6204
EEE     S&E       R&D       TOTAL

 0       0         S315K      $315K
                                      31

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PROJECT 12:  TOX1COLOGICAL EFFECTS OF YOC MIXTURES IN ANIMAL AND
               mvnjto SYSTEMS

A.   Objectives:

     Explore several aspects of the potential health impact of VOC mixtures: are there systemic
     (immunological,  reproductive,  neurobehavioral)  effects of VOC exposures mat are
     detrimental to animal health; do offgas VOCs induce irritant effects in animal lungs; do
     these same VOCs induce mutagenic alterations in experimental in vitro systems; and can
     a matrix approach to VOC mixtures be constructed that will aid in assessing mixture
     toxicology due to additivity or interactions?                             ';,

B.   Background:                j                                       <•

     Offgas VOCs emitted from a variety of construction materials and new synthetic-based
     objects (e.g., furniture) appear to affect human neurobehavior and comfort. These VOCs
     may also induce more severe health effects due to their systemic redistribution in the body
     with resultant potential impacts on reproduction, fetal development, immunology, and
     respiratory cell function. Some of these VOCs also appear to be cytotoxic or mutagenic
     in special  bacterial systems lending credence to potential cytological effects, including
     transformation (cancer).  Since VOCs often occur as varying complex mixtures, we need
     to develop generic approaches to the assessment of the health impact from their exposure
     that can be used for any similar mixture.  Hence,  an integrated program of animal and
     in vitro toxicology is needed to pursue these research questions that are not amenable to
     human system study.

C.   Approach:

     Several approaches  will be used in different laboratory settings.  Use of an animal
     inhalation  facility will address  simple and complex exposure toxicology.  These initial
     studies will be hazard identification oriented, after which more detailed studies will be
     conducted. These chamber facilities will also be used to fulfill experimental designs that
     aim at dissecting questions of additivity or interaction of VOCs in a conceptual framework
     to develop generic approaches  to mixture study.   Also, in collaboration with AEERL,
     offgas  VOC irritancy  and  mutagenicity can be assessed to determine acute effects of
     exposure on breathing patterns as a bioassay system for relative potency as well as potential
     carcinogenicity of these gases or combinations.
D.   Milestones:

     •     Completion of respiratory irritancy bioassay

     •     Establishment of chamber exposure capability
10/90

10/90
                                         32

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     •    Initiation of systemic toxicity tests



     •    Completion of matrix study designs



     »    Completion of mutagenicity studies on offgas VOCs



£.   Project Contact:



     George Goldstein   (919) 966-6200
F.   Resources:
     FY90
                                   10/90



                                    6/91



                                    8/91
                     FTE     S&E
 R&D
$159. IK
 TOTAL
$159. IK
                                       33

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      INDOOR AIR SOURCE CHARACTERIZATION
                            & MITIGATION

FTEs
S&E
R&D
TOTAL

FY87
6.0
320.4
725.0
1045.4

FY88
8.0
398.0
840.0
1238.0

FY89
8.0
538.4
921.2
1459.6

FY90
8.0
904.3
823.8
1728.1
i
FY91
7.0
881.7
1579.8
2461.5

Benefits to be Derived:

Indoor Air Quality (IAQ) studies have shown that the levels of organic compounds and other
pollutants in  indoor environments exceed the levels found outdoors.  Exposure to indoor air
pollutants involves literally thousands of chemical compounds being emitted from  a multitude
of sources. Exposures occur in homes, offices, stores, schools, transportation systems, etc. A
number of fundamental questions need to be answered:  What compounds are being emitted?
What are the important sources? What are the indoor concentrations?  What are the effects on
the exposed individuals? Can the emissions be prevented? What IAQ control alternatives are
available?  Is IAQ control effective and how much does it cost?

     The research program on Indoor Air Source Characterization & Mitigation is designed to
answer many of these critical questions by: 1) developing an understanding of and data on the
compounds emitted and their emission rates for important indoor sources and 2) developing IAQ
control strategies, including comprehensive studies of indoor air cleaning devices.  The results
of the research will be used to provide public guidance, the cornerstone of EPA's IAQ policy.
The  information on sources will allow the public to make informed choices regarding the
selection and use  of products and materials used indoors.  Source test methods will be made
available to manufacturers to enable them to evaluate their own products and to promote the
production of low emitting materials.  Data on IAQ control devices will allow consumers to
select cost  effective IAQ control systems.
Historical Perspective:

Historically, concern over air pollution has focused on outdoor exposures.  EPA has mounted an
aggressive program to reduce emissions to the ambient air. Only recently has the environmental
community recognized that the indoor environment represents a major component of an
                                       34

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                                                                                                 1
individual's total exposure to air pollution.  In 1983, at the request of Congress, EPA began a
modest research program on indoor air pollution, mainly focusing on radon.  In 1986, with the
passage of SARA, Tide IV specifically mandated a Federal IAQ research program.

Since 198S, EPA has been conducting a research program aimed at the characterization of indoor
sources and methods of controlling indoor air pollution.  An integrated research approach for
source characterization has been developed, combining test chamber evaluations of sources, IAQ
test house studies, and IAQ models. Environmental test chamber methods have been developed
for determining the chemical composition and rate of emission from sources of indoor air
pollution, including consumer products, building materials, and unvented kerosene heaters. An
IAQ model has been developed  for predicting the time history of indoor concentrations of
specific pollutants at numerous locations in buildings.   The model has been tested with data
collected in the IAQ test house and has given good agreement between measured and predicted
indoor concentrations.

The "chamber-model-test house"  approach was successfully used to conduct a study requested
by the Office of Toxic Substances on emissions of perchloroethylene from dry cleaned clothing.
Program Office support also included emissions testing of carpet samples from Waterside Mall,
and the development of recommendations regarding "airing out" the carpet prior to installation
to reduce indoor emissions of 4-PC.

Research on IAQ control has focused on evaluations of devices designed to remove indoor
pollutants. Studies on  the effectiveness of activated  charcoal filters  showed poor removal
efficiency for low concentrations of organic vapors.  Filters designed to remove indoor particles
were evaluated to determine removal efficiency as a function of particle size.  Information in all
research areas has been exchanged with interested parties, including: ASHRAE, ASTM, local
and state governments,  and  the  public.  Manufactures of building materials and consumer
products have been particularly interested in the test methods being developed. This interest has
been translated into increased private activity in the source testing area. It is anticipated that this
will eventually lead to the development and marketing of low-emitting materials and products.
Fiscal Year 1989:

Research on the evaluation of indoor sources continued to mature in FY89.  Small-chamber
testing methods developed by EPA were prepared and submitted to ASTM for publication as a
Standard Guide.  An EPA report on these testing methods was also published.  Research was
initiated  to develop  rate constants for adsorption to and desorption  from indoor "sinks".
Preliminary studies of consumer products included testing of aerosol products, as well as air
fresheners and room deodorants. The primary purpose of these studies  was to develop testing
methods  that can be used for exposure assessment.  An international study to compare testing
methods was conducted jointly with leading European IAQ research establishments.  Technical
support was provided to OARM's "Project 1992" through chamber evaluations of office partition
                                          35

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panels and an architectural coating product. The IAQ model was expanded to include predictions
of occupant exposure (both instantaneous and  cumulative) based  on activity patterns.   A
computerized data base on indoor sources was completed.  Additional research on kerosene
heaters included chamber studies and field measurements in mobile  homes, with the focus on
indoor particles.  Continued work on particle filters was conducted, including evaluation of
ozone generation by electrostatic precipitators.

Fiscal Year 1990:

Indoor source evaluations via small chamber  testing  will be continued at a  modest pace.
Candidates for testing include: carpets, wall coverings, paints, waxes/polishes, caulks, adhesives
and remitting sinks such as old carpets and ductwork liners from heating, ventilating, and air
conditioning (HVAC) systems. Expansion of source characterization research in FY91 to include
sensory irritation response will be planned in FY90, in a cooperative project with EPA's Health
Effects Research Laboratory. Mathematical models of source emissions and "sink effects" will
be developed.  They will be incorporated into the IAQ model, which will be further enhanced
by improving the user interface and increasing the speed of the solution algorithms. IAQ test
house studies will focus on fast decaying, solvent based products (e.g., stains, varnishes,  and
waxes). This research will provide information useful to consumers on usage practices that will
reduce exposure to solvent emissions.  Research on air cleaners will  focus on the development
of appropriate testing methods for indoor particle filters. Cooperative work with ASHRAE will
include development of methods for determining ventilation effectiveness.  An international
workshop on indoor source' characterization  will be conducted for  the exchange of  research
results with worldwide experts. Technical support to EPA Program Offices will be provided as
needed.
Fiscal Year 1991:

This year will be the first year when source characterization methods developed during FY84-
90 will be used to generate information on emissions from a broad range of indoor sources. It
will  also be the first year of testing emissions by bacterial  and animal assays for direct
measurement of relative health and comfort effects of the complex mixtures emitted by indoor
sources.  This information will be used to compile lists of low emitting materials and products.
Such lists will be used to rank materials vis-a-vis their impact on indoor air quality.  The first
edition of a "Guidance  Manual on the Testing, Selection, and Use of Indoor Materials  and
Products" will be drafted.

Prior to FY91, only limited research will  have been conducted to support indoor air quality
control and mitigation.   In FY91, an expanded research program will be directed to designing
and evaluating control devices and mitigation strategies. Research on air cleaning devices will
be expanded by: 1) developing and testing improved designs for particle air cleaners;
                                          36

-------
2) conducting R&D on new concepts for removing vapor-phase organics from indoor air; and 3)
evaluating the cost-effectiveness of cleaning outdoor air used for ventilation, in situations where
it doesn't meet NAAQS's (a major problem for meeting ASHRAE Standard 62 in some cities).
This research will result in recommendations on air cleaners, ventilation strategies, and methods
for modifying or treating indoor sources to reduce emissions.
                                         37

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PROJECT 13: INDOOR AIR SOURCE CHARACTERIZATION

A.   Objectives:

     Develop emission testing procedures for sources of indoor air pollutants, including building
     materials, consumer products,  combustion  devices,  and biocontaminated materials.
     Evaluate the effect of environmental parameters (e.g., temperature, humidity, air exchange
     rate)  and use  parameters (e.g.,  material  loading,  fuel rate) on  source emission
     characteristics.  Develop emission factors for both total and individual components, and
     provide a data  base of  source  emission  factors.  Design  source emissions  models
     incorporating fundamental mass transfer processes.  Develop a fundamental understanding
     of the "sink"  effect (adsorption/desorption) of various building materials and furnishings
     and rate data for these processes. Develop and evaluate,  as a joint effort of the engineering
     and health research laboratories, techniques for determining occupant responses to organic
     emissions from indoor sources.

 B.  Background:

     Information on the emission characteristics of indoor sources is needed to assess occupant
     exposure to the wide variety of pollutants encountered in indoor environments. Emission
     factors are coupled with IAQ models to determine indoor concentrations of both total and
     individual compounds,  and biocontaminants. Available information  on source emission
     characteristics is limited to a few  sources, and methods  for determining source emissions
     are still being developed.  The effects'of environmental variables on emission rates are
     generally understood, but quantitative data are required. Mass transfer source emissions
     models based on physical and chemical processes and  properties are also needed.  The
     effects of indoor sinks  are known to affect the concentration vs. time profiles of indoor
     pollutants, but quantitative data are needed to fully describe this phenomenon.

     The occupant exposure profile developed from the source emission factors and IAQ model
     calculations will be useful in developing IAQ risk assessments based on known health
     effects.  In addition, methods are needed to determine other types of occupant responses
     (e.g., irritation, discomfort) to indoor sources.
                                          38

-------
C.   Approach:
     Development of procedures for evaluating source emission characteristic will occur, for the
     most part, in test chamber facilities.  Small environmental chambers are available on-site
     for testing many sources of indoor air pollutants.  Large chambers needed for testing
     combustion sources can be accessed through an existing cooperative agreement.  An IAQ
     test house is available for evaluating activity sources and for confirming chamber results
     obtained for other source types.  Chamber testing is also required to evaluate the effect of
     environmental and use  parameters on  emission rates.   Both theoretical analyses and
     chamber tests are needed to develop mass transfer source emission models and to elucidate
     "sink" effects. Methods for evaluating occupant responses (irritation, discomfort) to indoor
     sources are  under development in Europe, but progress in the  U.S. has been slow.
     Potential techniques  include:   chamber or test  house human response studies using
     questionnaires and neurotoxicity test batteries; animal  studies to evaluated respiratory
     irritation; and odor panels.  Panels of evaluators could be used to develop "olf" and
     "decipol" values per Fanger's research.  In FY90 researchers in this source characterization
     project will work with researchers in the lexicological effects project (Project 12) to select
     available methods for sensory irritation  testing,  for  evaluation in FY91 as  source
     characterization/product testing methods.
D.   Milestones:
           Submission of small chamber testing guide to ASTM for approval

           Publication of paper on "sink" effects

           Publish paper on mass transfer source model

           Selection of potential occupant response methods for evaluation
           inFY91
                                                          11/89-

                                                           2/90

                                                           3/90

                                                           6/90
£.   Project Contact:

     W. Gene Tucker
       (919) 541-2746
       (FTS) 629-2746
F. -  Resources:
     FY90
                                 S&E
                      R&D
6.0
S504.3K    S507.6K
                           TOTAL
S1011.9K
                                          39

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PROJECT 14: INDOOR AIR QUALITY CONTROL

A.   Objectives:

     Develop indoor air quality (IAQ) models useful for predicting occupant exposure to indoor
     air pollutants.  Evaluate and develop air cleaner technologies applicable to the removal of
     particulate and vapor-phase indoor air pollutants. Determine the effectiveness of ventilation
     strategies, including HVAC operation options, as a means of improving indoor air quality.
     Evaluate  and develop  source  control options for reducing  emissions  from material,
     combustion, activity, and outdoor sources.

B.   Background:

     Three basic strategies are available for controlling levels of indoor pollutants: modifying
     emissions from indoor sources; removal of indoor pollutants using air cleaners; and  altering
     indoor concentrations by improving ventilation practices.  Evaluation of the effectiveness
     of these strategies, singly or in combination, requires the application of an IAQ model.
     EPA's IAQ model (Version 1.0 was published as EPA-6QO/8-88-097a,b; Version 1.75 was
     current at the end of FY89) predicts the time history of indoor concentrations for specific
     pollutants based on:  source  characteristics and emission  factors; ventilation parameters,
     including air exchange rate; HVAC operation, and room-to-room air movement; and air
     cleaner effectiveness. The model also considers the effect of "sinks".  Further research is
     needed to refine the model, including improvements in the user interface, modifications of
     the solution algorithms to increase computational speed, and refinements in the source and
     sink terms to account for new research findings.

     Evaluations of air cleaner effectiveness conducted to date have provided performance data
     on particle removal efficiency of filters with various ASHRAE ratings for given particle
     size ranges.  Evaluation of organic vapor controls has been limited to activated carbon.
     These tests showed carbon to be generally ineffective as an  IAQ control medium for low
     concentrations of organic vapors.  Additional research is  needed to evaluate and  develop
     effective  techniques for removal of particulate and gaseous indoor pollutants.   Ozone
     generation by various types of air cleaners is also an important issue  needing further
     research attention.  Ventilation  strategies for improving IAQ include dilution and  flushing
     via increased air exchange rates, local or spot ventilation for specific sources (e.g., smoking
     lounge, copying room), and  delivery of fresh (outside) air to specific building locations.
     A major  problem in  evaluating  these strategies  is the  determination of ventilation
     effectiveness (i.e., the efficiency of the HVAC system in distributing fresh air). Thus,
     research is needed to improve methods for measuring ventilation effectiveness. There are
     also many options for source control that need to be addressed.  Among these are  material
     conditioning, building "bake-out", and control of soil gas entry (which can be a source of
     pesticides, components  of hazardous wastes, or excessive moisture).
                                          40

-------
C.   Approach:
                                                                t
     Research to improve  the IAQ model will be conducted both in-house and through a
     cooperative agreement.  The in-house effort will focus on  improving the model as a
     research tool for evaluating the relationship between sources and indoor concentrations, and
     will include refinement of the source and sink terms. The extramural work will emphasize
     improvements in the user interface and solution algorithms. A new version of the model
     that predicts exposures from source emissions will also be produced.  Research on air
     cleaners will be  conducted at the laboratory and pilot  scale through a cooperative
     agreement.   An  in-house  laboratory  will  be equipped with  sufficient  measurement
     capabilities to conduct limited experiments on air  cleaners.  Work on improving methods
     to measure ventilation effectiveness will be conducted cooperatively with ASHRAE.  A
     feasibility study will be conducted on control of soil gas contaminants and moisture by
     subslab ventilation techniques that were developed for radon control. All of these efforts
     will be conducted at modest levels of activity, with emphasis on methods development and
     facility preparation for expanded testing (especially of air cleaners) in FY91 and beyond.
D.   Milestones:

     Completion of Version 2.0 of the IAQ model

     Completion of Exposure Version of IAQ Model

     Publication of report on air cleaner effectiveness

     Completion of feasibility study of controlling soil gas contaminants
     soil gas contaminants

     Publication of report on; strategies for improving ventilation
     effectiveness
 3/90

 6/90.

 8/90

10/90


11/90
                                          41

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E.  Project Contact:

    W. Gene Tucker


F.  Resources:



    FY90
(919) 541-2746
(FTS) 629-2746
   S&E       R&D
2.0
  $400.0K    $316.2K
TOTAL

S716.2K
                                     42

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APPENDIX E

-------
EPA INDOOR AIR RESEARCH PROGRAM FOR
          FISCAL YEAR 1991
             JULY 1,1990

-------
EPA INDOOR AIR RESEARCH PROGRAM FOR FISCAL YEAR 1991
                                CONTENTS


            INDOOR AIR PROGRAM MANAGEMENT & TECHNOLOGY
            TRANSFER

  Project  1:  Indoor Air Program Management and Coordination

            INDOOR AIR HEALTH IMPACT AND RISK ASSESSMENT

  Project  2:  Risk Characterization Methodology and Risk Assessment
            for Noncancer Endpoints

  Project  3:  Characterization of Biocontaminants in Indoor Air and
            Associated Health Risks

  Project  4:  Indoor Air Quality Test Kit

  Project  5:  Publication of the Indoor Air Pollution Reference Bibliography

            INDOOR AIR SOURCE CHARACTERIZATION AND MITIGATION

  Project  6:  Methods Development for Indoor Air Source Characterization

  Project  7:  Indoor Air Source Characterization Research

  Project  8:  Methods Development for IAQ Control Evaluations

  Project  9:  Evaluation of Air Cleaners for IAQ Control

  Project 10:  Evaluation of Ventilation for IAQ Control

  Project 11:  Evaluation of Source Management Options for IAQ Control
Page
   7

   9



  10

  12

  14

  16

  18

  20
            INDOOR AIR BUILDING STUDIES AND METHODS DEVELOPMENT

  Project 12:  Indoor Air Quality Assurance                                     22

-------
                                                                            Page
Project 13:  Compendium of Indoor Air Quality Methods

Project 14:  Monitoring Methods Development

Project IS:  Analytical Methods Development
                                                \
Project 16:  Demonstration Studies                 t

Project 17: , Large Building Exposure Assessment     ?<
                                                                              24

                                                                              26

                                                                             .28

                                                                              30

                                                                              32
            INDOOR AIR HEALTH EFFECTS
Project 18:  Characterization of Human Responses to Complex Mixtures
            of Volatile Organic Compounds

Project 19:  Toxicological Effects of VOC Mixtures in Animal
            and In Vitro Systems

Project 20:  Biological Markers for Environmental Tobacco Smoke
            Exposure and Dosimetry

            BIOCONTAMMATION ASSESSMENT

Project 21:  Assessments of Microbiological Program Hazards in the
            Indoor Air Environment

Project 22:  Modeling and Monitoring Design for the Retrieval of
            Microorganisms in Indoor Air Environments
                                                                              34
                                                                              37
                                                                              40
                                                                              43
                                                                              46
                                       11

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INDOOR AIR PROGRAM MANAGEMENT &
      TECHNOLOGY TRANSFER

-------
PROJECT 1:  INDOOR AIR PROGRAM MANAGEMENT AND COORDINATION
A.   Objectives:

     Manage the ORD Indoor Air Research Program by coordinating the indoor air research
     efforts of participating ORD laboratories; coordinate the indoor air research activities of
     other Federal agencies.

B.   Background:

     Title IV of the Superfund Amendments and Reauthorization Act of 1986 authorizes EPA
     to conduct  an  indoor air research program.  The Act  also  gives the  Agency  the
     responsibility for coordinating the indoor air research activities for all Federal agencies.
     EPA has designated a Matrix Manager for carrying out these responsibilities.

C.   Approach:

     The Matrix Manager directs the EPA Indoor Air Research Program through a steering
     committee that represents both the participating ORD laboratories and ORD headquarters
     offices. The research program focuses on the risk assessment of indoor environments and
     conducts research in the areas of risk assessment methodology, monitoring and modeling,
     health effects, and mitigation techniques. Other specific projects are conducted under the
     direction of the Matrix Manager.

     Through the interagency Committee on Indoor Air Quality, the Matrix Manager coordinates
     the indoor air research activities of the other Federal agencies.

D.   Products:
     Program Management:

     •     Conference/workshop support for indoor air topic

     •     Report on the EPA Indoor Air Research Program

£.   Project Contact:

           Michael A. Berry  (919)541-4172
                            (FTS) 629-4172
7/91

9/91

-------
F.  Resources:
                            S&E
                   R&D
    FY91
1.0     S103K
$102K

-------
INDOOR AIR HEALTH IMPACT AND RISK ASSESSMENT

-------
PROJECT 2:  RISK   CHARACTERIZATION   METHODOLOGY   AND   RISK
                             FOR NONCANCER ENDPOINTS
A.   Objectives:

     Continue development of the risk characterization methodology to consistently assess
     noncancer health effects associated with different indoor air pollution exposure scenarios;
     incorporate standard EPA guidelines and newly emerging methods;  develop methods for
     assessing exposures to both single compounds and mixtures; apply this methodology to
     specific  indoor  air problems; apply  time-activity patterns  to a single compound, and
     mixtures; evaluate health effects and index approaches for  complex mixture exposures;
     compare several quantitative noncancer risk assessment techniques using the framework;
     and obtain  distributions for values in each of the columns and investigate alternative
     representations of overall uncertainty.

B.   Background:                                  f

     Noncancer  health effects have been associated  with  indoor air pollution problems as
     evidenced by Sick Building Syndrome  symptoms.  For EPA to determine the potential
     health risks presented by indoor air pollution, a methodology is needed to characterize all
     health risks  presented by each pollutant, including noncancer effects.  There is  little
     agreement on standard noncancer risk assessment methods for individual compounds, and
     even less for complex mixtures. Once candidate methods are developed and the extent of
     noncancer health problems assessed, research priorities can be identified. This information
     can then be made available for advising the public, and the need and effectiveness of
     mitigation measures can be assessed.

C.   Approach:

     Apply the newly developed risk characterization methodology to specific pollutants and
     indoor air pollution problems.  Use existing data to verify and/or  refine several of the
     approaches identified in the initial phases of this project.  Data sources are sparse but may
     include:  chamber studies  with human exposures, survey  data from sick  buildings,
     monitoring data  from problem buildings, animal toxicity studies, and emissions testing and
     modeling. Results of these risk determinations for specific pollutants or problem buildings
     will be published.  The risk characterization framework will be used to compare several of
     the emerging quantitative techniques for a specific pollutant.

-------
D.   Products:
     t    Identification and review of available health effects data
     •    Application of time-activity to a single compound
     *    Completion of refined testing of health effect and index approaches
     •    Comparison of several techniques for a single compound
E.   Project Contact:
     Michael A. Berry  (919)541-4172
                      (FTS) 629-4172
                                                       11/90
                                                        3/91
                                                        5/91
                                                        9/91
F.   Resources:
     FY91
1.0
 S&E
$103K
 R&D
$175K

-------
PROJECTS:  CHARACTERIZ ATION OF BIOCONTAMINANTS IN INDOOR AIR AND
              ASSOCIATED HEALTH RISKS
A.   Objective:

     Continue development of a comprehensive review document on biocontaminants in indoor
     air.

B.   Background:

     A cooperative effort has been undertaken with EPA/ECAO-RTP to assess the potential
     health risks presented by biocontaminants in indoor air.  This effort has taken the form of
     a preliminary review of bioaerosol literature, as well as draft technical manuscripts on
     airborne mycotoxins and the use of biocides as a mitigation technique.

C.   Approach:

     The preliminary review will provide the framework for proceeding with the comprehensive
     review document on biocontaminants in indoor air. The document will evaluate and assess
     scientific information on the health and welfare effects associated with exposure of different
     populations to various types, concentrations, and mixtures of biological pollutants in a
     variety of indoor environments.  Scientific  data on environmental monitoring  will be
     evaluated  to provide a better understanding of these pollutants in the indoor environment.
D.   Products:

       •   Consensus report on document form and substance

       •   Draft of first half of comprehensive review document
           to include analysis of pollutant/concentration,
           exposure/setting, and exposure assessment

       •   Draft of second half of comprehensive review document
           to include source/factors, health effects, and
           dose-response relationships

E.   Project Contact:

     Michael A. Berry  (919) 541-4172
                      (FTS) 629-4172
 2/91

 6/91



12/91

-------
F.  Resources:
    FY91
FTE     S&E       R&D




0.5     $52K      S150K

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                                                                                                I
PROJECT 4:  INDOOR AIR QUALITY TEST KIT
A.   Objective:

     Develop a versatile, portable, and comprehensive test kit to be used for the screening of
     indoor air quality problems during an initial walk-through.

B.   Background:

     It is often difficult for an investigator to recommend an appropriate intensive indoor air
     study  without the benefit of screening data.  An IAQ test kit can be utilized to provide
     environmental information that can be used in the design of an in-depth investigation or in
     determining the actual need for further studies.                                    1

C.   Approach:

     Determine the components of test kit so that it is compact, relatively inexpensive, and will
     provide a rapid indication of environmental problem areas requiring intensive monitoring.
     Indoor air quality test kit elements may include:         	

           IAQ monitor for CO2, temperature, and humidity, with memory and printer
           Aerosol dust monitor          "
           Formaldehyde monitor with analysis
           Organic solvent sampling tubes
           Radon monitor
           Smoke tubes
           Screening detector tubes (CO, NO2, CO2, SO2) and pump kit
           Digital micromanometer and velometer
           CO monitor
           Dip slides for microbial sampling of fluids
           Sterile tubes, pipets, and bulb for collection of environmental samples for microbial
           analysis
D.   Products:
       •   List of test kit components

       •   Complete test kit

       •   Evaluation of test kit under field conditions
12/90

 2/91

 4/91

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£.  Project Contact:

    Michael A. Berry   (919)541-4172
                     (FTS) 629-4172
F.  Resources:
    FY91
FTE     S&E       R&D

0.25    $25K       $25K
                                      8

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PROJECT 5:  PUBLICATION OF THE INDOOR AIR REFERENCE BIBLIOGRAPHY
A.   Objective:

     Publish the Indoor Air Reference Bibliography, which includes citations on all aspects of
     indoor air pollution.  This information  will assist researchers in identifying available
     information dealing with a specific area in indoor air pollution.

B.   Background:

     The Indoor Air Pollution Reference Bibliography is an extensive compilation of reference
     materials on indoor air pollution.  Because this is an area of rapidly expanding research,
     it is necessary to continually search and retrieve publications from the scientific literature
     in order to maintain a current data base.

C.   Approach:

     As new  information is retrieved and evaluated,  it is incorporated  into the reference data
     base, which contains over 4,000 references. The citations are indexed on key works so that
     published articles can be identified in specific areas.
D.   Products:

     Publication of Indoor Air Reference Bibliography

E.   Project Contact

     Beverly Comfort   (919) 541-4165
                       (FTS) 629-4165
                                                          9/91
F.   Resources:


     FY91
FTE     S&E       R&D

0.25     $25K       $15K

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INDOOR AIR SOURCE CHARACTERIZATION
          AND MITIGATION

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PROJECT 6:  METHODS   DEVELOPMENT   FOR   INDOOR   AIR  SOURCE
              CHARACTERIZATION
A.   Objectives:

     Continue development of methods for chemically and physically characterizing emissions
     from sources of indoor air pollutants.  Initiate development of biological response-based
     methods for screening emissions and certifying indoor materials and products.

B.   Background:

     Considerable progress has been made in developing methods for chemically characterizing
     emissions from indoor sources. lexicological interpretation of the emissions data is very
     difficult,  however, and evaluating the health or comfort acceptability of sources (even on
     a comparative basis) is tenuous.  Biological response-based testing methods hold promise
     of giving more direct indications  of product acceptability.

C.   Approach:

     The major new thrust of this project in FY91 will be to initiate evaluations of biological
     response-based methods for testing the potential health and comfort effects of emissions
     from sources of indoor air pollutants'. Currently available methods using humans, animals,
     and cellular  or biochemical  in  vitro  assays will be considered.  Such methods  will
     supplement chemical analyses of emissions that have been developed in this project since
     FY84, and will improve our ability to predict the acceptability of gaseous, paniculate, and
     biocontaminant emissions from indoor sources. The methods developed must be usable by
     private-sector manufacturers and testing organizations that will be involved in screening
     and certifying products.

     A collaborative project involving researchers from EPA's indoor air  research program,
     Aarhus University, and the J.B. Pierce Laboratory will be conducted at Yale University in
     FY91.  An  international conference  on chemical and biological methods for source
     characterization will be held,  followed by a series of specialty seminars on potential new
     methods for evaluating the health and comfort acceptability of indoor sources. A research
     plan will be prepared for further scientific investigations of biological mechanisms by
     HERL, and development and demonstration  of product screening methods by AEERL.
     Refinement of chemical characterization methods  for ASTM approval and private sector
     use will be continued concurrently. Ongoing development of methods for sources such as
     maintenance activities and use of consumer products will also be continued.
                                         10

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D.   Products:
           R&D priorities for response-based source testing methods

           Source characterization conference proceedings published

           Preliminary procedures for testing activity sources
           (e.g., vacuum cleaning)

           Chemical emission characterization methods for caulks and
           sealants to ASTM for approval
                                                          6/91

                                                         10/91

                                                         11/91


                                                          6/92
E.   Project Contact:
     Gene Tucker
F.   Resources:
     FY91
 (919) 541-2746
 (FTS) 629-2746
FTE     S&E

1.5      S150K
 R&D

$300K
                                         11

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PROJECT 7:  INDOOR AIR SOURCE CHARACTERIZATION RESEARCH
A.   Objectives:

     Evaluate the effect of environmental parameters (e.g., temperature, air exchange rate,
     humidity,  light) and  use parameters (e.g., amount and  frequency of product use) on
     emission rates from sources. Develop an understanding of the "sink" effect (sorption and
     reemission of pollutants) of indoor surface materials.  Develop an understanding of the
     effects of environmental and source conditions on growth and viability of biocontaminants
     on indoor materials, and their dispersion into indoor air.

B.   Background:

     Research to date has shown that temperature is generally the most important environmental
     parameter  affecting emissions.  Very little research on use parameters has been done.
     Chamber studies on sink effects were begun in 1989,  and preliminary data published in
     1990.

C.   Approach:

     Controlled studies of sources and sink effects will be continued in laboratory chambers at
     EPA and other facilities.  Chamber studies of biocontaminant growth on materials -will
     begin in 1991.
D.   Products:
       •   Models describing effects of environmental and use
           parameters on emissions

       •   Revised IAQ model for estimating exposures to
           emissions from sources

       •   Revised data base of sources, compositions, emissions,
           sink effects, and potential exposures

       •   Research report on effect of environmental and source
           conditions on biocontaminant viability and growth on indoor
           surface materials
6/91


7/91


9/91


9/92
                                         12

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£.   Project Contact:

     Bruce Tichenor


F.   Resources:


     FY91
      (919) 541-2991
      (FTS) 629-2991
1.0
 S&E

$200K
 R&D

$450K
                                      13

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PROJECT 8:  METHODS DEVELOPMENT FOR IAQ CONTROL EVALUATIONS
A.   Objectives:

     Continue development of EPA's IAQ model, to enable comparisons of exposure reductions
     and costs of IAQ control options.  Develop methods for testing the effectiveness of air
     cleaners in reducing exposures to particles and organic vapors.

B.   Background:

     The current IAQ model, under development since 1986, is being modified to account for
     the "sink" effect of indoor surfaces, and to calculate occupant exposures to pollutants (as
     well as indoor concentrations).  This new version will be available to the public in 1990.
     Current methods for evaluating the performance of air cleaners do not satisfactorily account
     for size distributions of indoor particles.  They also do not account for constant or time-
     dependent sources of emissions.

C.   Approach:

     Modification of the IAQ model to refine exposure estimates for various types of sources and
     occupant activity patterns will be continued by in-house staff. Contract and in-house studies
     will be conducted to develop appropriate test dusts  for evaluating the performance of*air
     cleaners for particles, and improved testing procedures for both particulate and gaseous air
     cleaning devices and systems.

D.   Products:
E.
  •   Revised IAQ model (Version 3.0) for comparing options for
      IAQ control

  •   Test methods for air cleaners to ASTM for approval

Project Contact:

Leslie E. Sparks    (919) 541-2458
                  (FTS) 629-2458
                                                                              10/91

                                                                              12/91
                                         14

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F.  Resources:
    FY91
EH     S&E      R&D




1.2     $100K     $230K
                                   15

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PROJECT 9:  EVALUATION OF AIR CLEANERS FOR IAQ CONTROL
A.   Objectives:

     Evaluate the effectiveness of commercially available devices for removal of particles and
     gases from indoor air.  Determine the positive or negative effects of air cleaners on the
     control or growth of biocontaminants and other potentially negative side effects of air
     cleaners, such as ozone generation.  Develop improved air cleaning devices and systems.

B.   Background:

     Using air cleaners to remove paniculate or gaseous pollutants from indoor air (or from
     outdoor air brought into the building by an HVAC system)  is an option where source
     control and  improvements in  ventilation are insufficient.  These  devices can be free-
     standing in  a room, or installed  in the ductwork of an air handling system.   Most
     commercially available air cleaners are designed to remove particles; none are capable of
     gaseous pollutant removal for normal home or office building situations.

C.   Approach:

  .   Performance tests of commercially available devices were begun in laboratory facilities at
     the Research Triangle Institute in FY90.  This testing will be continued and expanded in
     both RTI  and EPA  laboratory  and test house-facilities in  FY91.   Improved  testing
     procedures will be used as they are developed under EPA and ASHRAE sponsorship.
     Experiments to determine conditions that promote growth of biocontaminants on air filters,
     and  their  dispersion into indoor air, will be started in FY91.  Field  testing  of the
     effectiveness and costs of devices and systems will be initiated as soon as resources allow,
     but probably no sooner than FY92.  New concepts for gaseous or particulate pollutant
     control that are developed by the private sector will be evaluated in controlled experiments
     as devices or systems approach commercial availability.
D.   Products:
           Summary report of air cleaner testing results

           Preliminary report on biocontaminant growth on, and
           dispersion from air filters
10/91
11/91
                                         16

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£.   Project Contact:

     Leslie Sparks
F.   Resources:
     FY91
 (919) 541-2458
 (FTS) 629-2458
FTE     S&E

1.0     $150K
 R&D

$300K
                                      17

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PROJECT 10: EVALUATION OF VENTILATION FOR IAQ CONTROL
A.   Objectives:

     To evaluate and develop guidance on ventilation effectiveness (e.g., location of air supply
     and return registers to maximize exhausting and diluting of pollutants).  Develop design
     guidance "on avoiding  materials  in  ventilation  systems  that  promote  growth  of
     biocontaminants, or act  as sinks that reemit and become major sources of indoor air
     pollutants.  Produce engineering design guidance on materials and systems for control of
     humidity and moisture in buildings to reduce indoor levels of biocontaminants.  Support
     improvements in private-sector standards for ventilation practices, such as ASHRAE
     Standard 62.

B.   Background:

     Extensive research has been done on ventilation rates of buildings, especially in connection
     with energy conservation. The practice of mechanically ventilating commercial buildings
     for  thermal  comfort and IAQ control (by diluting and exhausting pollutants) is well
     established,  if not completely  well understood.  Better information is needed on the
     distribution of ventilation air, and how it affects ventilation effectiveness. The importance
     of ventilation systems as sources of chemical and biological contaminants also needs to be
     better understood.

C.   Approach:

     Projects on ventilation effectiveness and ventilation system design to avoid creating sources
     of indoor air pollutants will  be undertaken jointly with ASHRAE, through an existing
     cooperative agreement. These laboratory and field projects will produce practical guidance
     on ventilation strategies that provide IAQ benefits, as well as comfort, at reasonable costs.
     As resources allow, novel techniques for ventilation  such as displacement flow designs
     (e.g., floor supplies and ceiling returns) and microenvironmental workstations (with
     individual control of ventilation, temperature, humidity,  lighting, and noise) will  be
     evaluated.  Evaluations of biocontaminant control by use of biocides or disinfectants (e.g.,
     UV light) will also be conducted as  resources allow.
                                          18

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D.   Products:

       •   Preliminary report on materials for HVAC systems that mitigate
           growth of microbial contaminants and emission of other
           pollutants

       •   Proposed ASHRAE Standard for ventilation effectiveness

£.   Project Contact:

     Leslie Sparks      (919)  541-2458
                      (FTS) 629-2458
                                                       10/91

                                                       12/91
F.   Resources:
     FY91
1.3
 S&E

$90K
 R&D

$100K
                                        19

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PROJECT 11:  EVALUATION  OF SOURCE MANAGEMENT OPTIONS FOR IAQ
               CONTROL         -
A.   Objectives:

     Evaluate options for reducing emissions from material sources by modification of product
     composition or application, or by conditioning before use in a building.  Evaluate options
     for modifying the design or operation of combustion sources to reduce indoor air pollutant
     exposures. Analyze options for reducing exposures from activity sources by modification
     of product design or method of use. Evaluate options for controlling outside sources by
     modifying routes of entry into buildings.                   j
                                                           i
B.   Background:                                          i

     Control of sources is often the  most effective way to improve indoor air quality. Results
     from source  characterization research  can be used to evaluate the cost-effectiveness of
     various types of source modifications or controls.

C.   Approach:                   	

     Laboratory and test house studies will be conducted to test the effectiveness of conditioning
     materials by  airing out or baking out.  Similar types of experiments will be conducted on
     combustion sources to determine the impact of use patterns on exposures to emissions from
     space heaters. Experiments in laboratories and test houses will also be run to determine the
     controllability of activity sources (e.g., exposures from the use of aerosol spray,  pump
     spray, and other application methods will be compared). Field studies of controlling outside
     sources will be conducted (e.g., to test the effectiveness of radon control techniques on soil
     gases contaminated by waste sites or leaking underground storage tanks).
D.   Product:
           Summary report on results of evaluations of source
           management options
                                                       10/91
E.   Project Contact:
     Bruce Tichenor
(919) 541-2991
(FTS) 629-2991
                                         20

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F.  Resources:
                   EH    S&E       R&D

    FY91          1.0     $191.7K    $199.8K
                                    21

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INDOOR AIR BUILDING STUDIES AND
    METHODS DEVELOPMENT

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PROJECT 12:  INDOOR AIR QUALITY ASSURANCE
A.   Objectives:

     Develop analytical QA standards to meet the specific needs of the Indoor Air Program,
     review past and planned Indoor Air Program monitoring studies, and establish lists of
     targeted indoor contaminants and concentrations.  Initial emphasis will be placed on the
     development of standards for vapor- and particle-phase nicotine, as well as other semi-
     volatile compounds collected on XAD-2, XAD-4, or PUP absorbents.

B.   Background:

     Quality assurance reference standards are an essential component of any monitoring and
     analytical study. Numerous reference standards have been developed for species commonly
     observed at high concentrations in ambient and indoor air. Significant research has been
     conducted to develop QA standards for volatile organic compounds collected by either the
     solid absorbent or canister monitoring method.   Although QA standards  for individual
     chemical species are normally commercially available, composite QA samples containing
     known concentrations of multiple target compounds mimicking environmental samples are
     not readily available.  In addition, QA reference standards are not readily available for
     newly developed sampling and analytical techniques.  Without external quality assurance
     data, routine indoor air investigation results are considered marginal.

     External QA is an essential component of any research program. The AEERL, AREAL,
     and HERL should continue to manage their internal QA  programs without a centralized
     external QA program. Without adequate external QA, the program may find it difficult to
     substantiate data quality. The Indoor Air Program must develop an independent external
     QA component that can support program research  needs and withstand peer review.
     Individual researcher and laboratory QA program costs should not be reflected as separate
     projects but be included with project costs.  The AREAL FY89 and FY90 QA projects
     are designed to develop external QA standard materials that can be utilized by all IAQ
     researchers.  In addition, EPA and NIST should collaborate to develop  QA reference
     materials that can be made available to federal, state, local, and private agencies in support
     of their indoor air programs.

C.   Approach:

     Primary emphasis will be placed on developing nicotine, formaldehyde and other aldehydes,
     and PUF/XAD-2 semivolatile QA standards.  Supporting FY91 IAQ monitoring and
     analytical programs through external audits coordinated with individual researchers, will
                                         22

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     also be stressed.  Developed standards will be validated and made readily available for
     monitoring programs.  Standards covering multiple concentration ranges will be prepared
     and evaluated to determine optimum analytical precision and accuracy. Compound stability,
     species and/or matrix interferences, and shipping/storage effects will also be evaluated.
D.   Products:

     •     Development of nicotine standards

     •     Development of SVOC standards

     •     Development of formaldehyde and other aldehyde standards

E.   Project Contact:

     Berne Bennett
                                                           1/91

                                                          9/91

                                                          9/91
 (919) 541-2366
 (FTS) 629-2366
F.   Resources:
     FY91
0.3
 S&E

$27K4
 R&D

$50K
                                         23

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PROJECT 13:  COMPENDIUM OF INDOOR AIR QUALITY METHODS
A.   Objectives:

     Compile the most commonly employed Indoor Air Quality monitoring and analysis methods
     into a standard-format compendium for distribution to participating Federal, state, local,
     and private agencies. The manual consists of monitoring procedures, analytical procedures,
     and a technical assistance document. Develop a Technical Assistance Document for indoor
     air, managers.
       -, A
B.   Background:
       y;
       .?!
     Previous attempts to standardize indoor air quality methodologies have been fragmented,
     inconsistent in format and/or technical information, or incomplete.  In addition, indoor air
     technology is rapidly emerging with many state-of-the-art monitoring and analytical
     techniques not fully evaluated and/or documented. Technical assistance documents assisting
     investigators in selecting when and how to employ indoor air procedures are not readily
     available.  As a result, indoor air quality data are not consistent among studies.  An EPA-
     sponsored compendium is needed which compiles the most commonly used monitoring and
     analysis methods. Once peer-reviewed, the universal-format procedures will be distributed
     to the public in a loose-leaf binder format that will allow for easy updating.

C.   Approach:

     Under contract, obtain indoor air methodologies and associated procedures employed by the
     user community.  Consolidate  the procedures, conduct a formal peer-review, produce
     initial and revised editions in a common format, prepare a companion technical assistance
     document, and distribute the compendium to the indoor air investigators.  Documents would
     be assembled to facilitate copy control and revision. A Technical Assistance Document will
     be published to assist IAQ investigators in the design and implementation of indoor air
     studies. Abbreviated compendium methods will be developed to facilitate the collection and
     analysis of IAQ samples in the field.
D.  Products:
           Peer review biological monitoring method

           Publish updated compendium

           Publish technical assistance document

           Publish abbreviated compendium methods
1/91

4/91

8/91

9/91
                                         24

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E.  Project Contact:

    Frank McHroy
F.  Resources:
                    (919) 541-2622
                    (FTS) 629-2622
    FY91
                   0.2
 S&E

$18K
 R&D

$100K
                                    25

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PROJECT 14: MONITORING METHODS DEVELOPMENT
A.   Objectives:

     Develop and evaluate integrated microenvironmental monitors simultaneously collecting
     particles, VOCs, SVOCs,  nicotine, and selected continuous parameters.  Develop and
     evaluate low-cost passive exposure monitors for use as screening and survey tools for
     selected parameters and personal exposure monitors for selected parameters.

B.   Background:

  1  Characterizing indoor environments and assessing  exposures requires the simultaneous
  (  collection of multiple contaminants over an extended time period.  Reviewing past data
     indicates that indoor air investigations are being conducted  using numerous screening,
     microenvironmental, and personal monitoring methods.  Each technique has its strengths
     and weaknesses.  Some produce data that are not directly comparable to existing data sets.

     Screening techniques are low in costs and unobtrusive, but are limited by experimental and
     analytical uncertainties.   On  the other hand,  personal monitor data better represents
     individual exposures. However, these techniques are limited to single or dual parameters,
     and may yield biased data resulting from PEM placement or usage by the participant.
     Microenvironmental monitors provide large  volume samples that support more detailed
     analysis.  When used in combination with other monitors, the resource requirements, noise,
     and obtrusiveness may result in altered participant lifestyles and activities.

     Improved integrated monitoring techniques are needed to better evaluate the overall impact
     of outdoor and indoor sources on the indoor environment and assess personal exposures.
C.   Approach:

     New and improved passive, personal, and microenvironmental monitoring techniques will
     be independently designed, developed, and evaluated.  Design parameter considerations
     include species to be collected, analytical requirements, sample media, quality assurance,
     resource  requirements, and obtrusiveness.   Additional field evaluation of previously
     developed low cost passive monitors for NO2, O3, VOCs, and SVOCs will be conducted
     to include side-by-side comparisons with certified methodologies. Prototype PEM particle,
     nicotine,  biological, and SVOC samplers will be designed, miniaturized,  developed, and
     evaluated. Prototype PEMs simultaneously collecting particles, nicotine, CO, and N02 will
     also be developed and evaluated.  The newly developed 20 pm sampler will be evaluated
                                         26

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     against standard flow SVOC samplers under field conditions. A low flow-rate compound
     annular denuder will be designed and tested to evaluate the phase distribution of SVOCs.
     Integrated microenvironmental monitors simultaneously collecting particles, SVOCs, VOCs,
     RH, T, biologicals, and criteria pollutants will be designed, developed, and field tested.
D.   Products:

     •     Upgraded PEM for NO2, CO, T, 03, and RSP

     •     Multipollutant microenvironmental sampler

     •     Prototype biological monitor

     •     Prototype acid aerosol monitor

     •     Develop and validate personal activity logger

E.   Project Contacts:

     Ross Highsmith   (919) 541-7828
                      (FTS) 629-7828
                                                         4/91

                                                         4/91

                                                         6/91

                                                         8/91

                                                         9/91
     Jim Mulik


E.   Resources:



     FY91
(919) 541-3067
(FTS) 629-3067
        S&E

        $45K
0.5
 R&D

$100K
                                         27

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PROJECT 15: ANALYTICAL METHODS DEVELOPMENT
A.   Objectives:

     Develop and evaluate analytical procedures for nontargeted polar and nonpolar organic
     compounds and personal sampling devices (PSDs).  Determine the precision, accuracy,
     species stability, interferences, and collection efficiencies of commercially available solid
     absorbents for organic compound classes.

B.   Background:

     A key decision in all1 indoor investigations regards which collection and analysis methods
     should be employed in the evaluation of indoor environments. The majority of the earlier
     research activities used solid absorbents for organic compound  collection.  Evacuated
     canister techniques are favored for VOCs.  Once the sample is collected, the investigator
     must again  choose between techniques for sample analysis. There is no single document
     that provides the investigator with the information needed to make the appropriate decision
     as to collection and analysis procedures.

     Analytical methodologies for ambient and source sample characterization are not always
     directly applicable to indoor air sample analysis, because these procedures may not provide.
     the sensitivity or selectivity required. Polar organics and marker compounds for numerous
     sources of suspected carcinogens are not routinely collected, extracted, or analyzed from
     indoor samples, regardless of collection media.  In addition, the physical  and  chemical
     characteristics of polar organics require extensive, and sometimes species-specific, sample
     preparation prior  to analysis. Changes in technology  may result in the formation and
     emission of compounds that were previously absent from the indoor air environment such
     as 4-phenylcyclohexene, which is associated with newly installed  carpet. In many cases,
     standardized analytical procedures do not exist for these new organic pollutants.

     The collection technique also affects the ability to analyze indoor air samples. Analytical
     procedures  employed for bulk samples are not directly applicable to detailed  chemical
     characterization of samples collected  at low flow rates, in particular, to PSD and PEM
     sample analysis. Improved analytical techniques for the identification and quantitation of
     chemical species,  both large- and small-volume samples, must be developed.   Research
     must be conducted to document  the strengths and weaknesses of the use of commercially
     available organic sampling media.
                                          28

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C.   Approach:

     Organic compounds (VOCs, SVOCs, PAHs, etc.) in indoor air samples will be chemically
     characterized  and quantified  to determine the stabilities of the species, the analytical
     precision and accuracy, and the potential interferences.   Polar and nonpolar organic
     compounds will be tested with improved procedures developed for collection, separation,
     detection, confirmation, and quantitation of specific species. Research will be conducted
     to determine the degradation products of polar organic compounds and their effects on the
     analytical results.  Marker compounds will be identified, and the target compound list will
     be updated. Enhanced analytical techniques for PSDs will be developed and compared to
     more standard analytical techniques, thus increasing the overall usefulness of low flow-
     rate devices in indoor monitoring programs.  Analytical methods will be developed and
     improved for  the identification and quantitation of both known and unknown compounds
     (biological contaminants). Research will be initiated to improve our understanding of the
     strengths and limitations of commercially available collection media and standard laboratory
     analytical methods for routine organic compound analysis.
D.   Products:

     •     Real time VOC analytical technique

     •'     Analytical procedure for polar VOC/SVOCs

     *     Analytical procedure for acid aerosols

     •     Analytical procedure for biologicals

£.   Project Contacts:

     Nancy Wilson     (919) 541-4723
                       (FTS) 629-4723
                                                          3/91

                                                          9/91

                                                          9/91

                                                          9/91
     Jim Mulik
     Resources:
     FY91
 (919) 541-3067
 (FTS) 629-3067
0.5
 S&E

$45K
 R&D

S150K
                                         29

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PROJECT 16: DEMONSTRATION STUDIES
A.   Objectives:

     Test and evaluate commercial and experimental IAQ program monitoring and analytical
     procedures used to evaluate indoor air quality in residences and office buildings. Develop
     revised  procedures  and  technical expertise for the evaluation of complaint  versus
     noncomplaint buildings.  Evaluate microenvironmental and personal source monitoring
     protocols in relationship to the measurement and analysis data necessary to conduct risk
     assessments.

B.   Background:

     Many indoor air investigations have been limited  in scope and technical conclusions
     resulting from the exhaustive resource requirements needed to simultaneously evaluate
     multiple environmental contaminants. Most investigations use preliminary surveys or easily
     identified sources as the basis for their study design.  Monitoring and analytical protocols
     were then aligned to support these best estimate hypotheses.  These approaches have been
     successful in simple environments where single or dual sources are known. The results of
     studies under more complex source and/or area conditions have not been as definitive.
     Modem office complexes are impacted by multiple environmental variables. Individual as
     well as  synergistic effects increase the difficulty in characterizing the air quality in these
     facilities.  SBS investigations require comprehensive monitoring, analytical, and  survey
     programs to fully characterize and quantitate the indoor environment and correlate these
     findings to exposures and risks. Additional research is needed to ensure that future indoor
     investigations provide the necessary data to support exposure and risk assessments.

C.   Approach:

     A comprehensive monitoring  study  will be conducted in up to  10 complaint and
     10 noncomplaint office buildings to characterize the indoor environment, correlate employee
     health related symptoms to environmental parameters, and develop strategies to improve the
     indoor air quality.  Particles, volatile organics, semivolatile organics, biologicals, and
     routine continuous measurements will be conducted daily at multiple locations over a one
     week period.  A multipurpose questionnaire will be develop to comprehensively assess
     personal and environmental parameters.   The questionnaire will be administered to all
     employees prior to sampling with supplemental questionnaires administered daily to selected
     employees  located in close proximity to the monitors.  The results will be analyzed to
     identify the parameters responsible for the  SBS implications.   Follow-up  studies  in
     additional high complaint office complexes will be conducted to validate the IAQ protocols
     and LOG results.
                                          30

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D.   Products:

     •     Standard diagnostic questionnaires and monitoring procedures

     •     Integration of EPA/NIST model with SBS

     »     Conduct of complaint and noncomplaint studies

E.   Project Contact:

     Ross Highsmith    (919) 541-7828
                      (FTS) 629-7828
                                                         1/91

                                                         4/91

                                                         9/91
F.   Resources:
     FY91
0.3
 S&E

$27K
 R&D

S513.5K
                                        31

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PROJECT 17:  LARGE BUILDING EXPOSURE ASSESSMENT
A.   Objectives:

     Develop protocols to evaluate the impact of single, multiple, and synergistic pollutants on
     the indoor air environment. Develop and validate mathematical models to analyze personal,
     physical, and chemical parameters and estimate short- and long-term health effects resulting
     exposures in the working environment.

B.   Background:

     Assessing health effects resulting from exposures to large building indoor air requires a
     multidisciplined understanding of the physical and chemical microenvironmental parameters.
     Past studies in high complaint indoor air environments have been plagued by limited
     resources that minimized the collection of data, assessment of exposure, and mitigation of
     sources.  Many of these studies have not been  able to correlate symptoms with the
     multivariable conditions.

     Advancements in monitoring and analytical methodologies, along with  improved building
     diagnostics  techniques and a better understanding of the health effects of single as well as
     multiple pollutants, necessitate the development of a comprehensive building assessment
 •  .  protocol. This protocol would analyze the total system to include building dynamics, air
     exchange  rate,   ergonomics,  temporal,  cumulative,   and  instantaneous  pollutant
     concentrations, and the  responses from individual workers.   These variables will be
     statistically analyzed to evaluate the health implications associated with short- and long-
     term exposures in the indoor air quality.

C.   Approach:

     A comprehensive protocol will be developed and tested under simple and complex indoor
     air environment conditions.  The protocol will be designed to collect the necessary data to
     fully evaluate the total building diagnostics and will include engineering, industrial hygiene,
     chemical, physical, biological,  and  personal components.   Statistical  models will be
     developed to estimate personal exposures and  propose mitigation processes.
D.  Products:
     •     Draft protocol

     •     Final protocol
           Initiate field study
1/91

8/91

9/91
                                          32

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E.  Project Contact:

    Ross Highsmith    (919) 541-7828
                     (FTS) 629-7828
F.   Resources:
     FY91
0.2
 S&E

$18K
 R&D

$400K
                                      33

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INDOOR AIR HEALTH EFFECTS

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PROJECT 18:  CHARACTERIZATION OF  HUMAN  RESPONSES  TO  COMPLEX
               MIXTURES OF VOLATILE ORGANIC COMPOUNDS
A.   Objectives:

     Characterize the dose-response relationship and time course of olfactory (odor intensity) and
     trigeminal (irritation) responses to a mixture of VOCs.  Ascertain the potential impact of
     upper airway inflammatory and pulmonary immune function responses on human health.
     Evaluate the effects of a chemical mixture on respiration in humans to obtain objective
     measures of respiratory irritation.  Develop measures of neurologic, respiratory,  and
     immune system responses to VOCs for use in discriminating between normal subjects and
     "hypersensitive" subjects or those exhibiting symptoms of "sick building syndrome" (SBS).

B.   Background:

     Growing  public awareness of the potential health hazards of chemicals  in  the indoor
     environment has helped identify a new problem known as "Sick-Building Syndrome" (SBS).
     Although the incidence of SBS complaints  has risen dramatically in the past  few years,
     reliable and objective methods to distinguish between SBS-responders and nonresponders
     have not been identified.  Congress recently mandated that EPA characterize the sources
     of and levels of exposure to VOC mixtures found in new buildings.  Common symptoms
     of sick building  syndrome include irritation of the  eyes, nose, and throat.  Affected
     individuals complain of headache, sinus congestion, and increased respiratory infections.
     A preliminary  Danish report of impaired short-term memory could  not be confirmed by
     recent studies, although  exposed individuals reported that exposure was aversive  and
     impaired their sense of well-being. SBS-affected individuals report similar experiences and
     impaired workplace performance.

     The above information suggests adverse impacts on olfactory and/or trigeminal nerves, the
     respiratory tract, and pulmonary immune system. Preliminary results from a  pilot study
     recently conducted suggest that VOCs cause an inflammatory response in the upper airways
     as indicated by an increase in neutrophils detected in the nasal lavage. Animal studies  also
     indicate that changes in respiratory patterns can be related to respiratory tissue irritation.
     Initial research will focus on the evaluation of immunotoxic effects and the assessment of
     respiratory irritancy in rodents and humans (see Project 19) following controlled VOC
     exposures in inhalation chambers. Elevated ambient levels of inhaled air pollutants have
     been associated with an increased susceptibility to respiratory viral infections, particularly
     in children. The socioeconomic impact of influenza viral disease is estimated at 3-5 billion
     dollars per year in the United States.  Viral upper respiratory tract infection has also been
     implicated as an important contributor to the etiology of asthma. The incidence and
                                         34

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     mortality associated with asthma  is increasing in the United States.  These objective
     measures of respiratory  irritation and immune  function  will complement subjective
     responses obtained in  similar VOC exposure experiments both here and in Europe and
     provide much needed data on human responses  to sick buildings and VOC mixtures.
     Additional investigation of neurobehavioral responses will continue.

C.   Approach:

     Three separate approaches to characterizing SBS will be taken.

     •     Neurologic responses -

           Since olfactory  and trigeminal responses to noxious stimuli are known to adapt at
           different rates, the selective contribution of these two senses can be assessed using
           psychophysical  and electrophysiological methods to characterize responses during
           prolonged VOC exposure.  In an ongoing study normal, healthy subjects are being
           exposed in a counterbalanced manner to a mixture of VOCs at four concentrations
           (0, 6,  12, 24 mg/m3) at weekly intervals.  Each exposure  will be for 3.5 hours.
           Subjective ratings of odor and sensory irritation will be obtained every 15 minutes
           to determine the time course of effects. In another experiment, subjects who report
           SBS symptoms  will be compared  with asymptomatic subjects.   Psychophysical
           methods will be used to assess the trigeminal response of subjects to a nonodorous
           chemical irritant (carbon dioxide).  It is hypothesized that SBS-subjects are more
           sensitive than  control subjects  to  mucosal irritation,  and  that trigeminal nerve
           irritation rather than olfactory stimulation is a key component of human response.

     •     Pulmonary Immune System Responses -

           Normal and sensitive adults will be  exposed to various concentrations of a complex
           mixture of VOCs to establish a dose-response relationship.  Nasal lavage fluid and
           cells and nasal biopsies will be analyzed for indicators of inflammation and allergy
           that may be associated with the SBS and that relate to disease. The indices to be
           surveyed  have  been  used  in  previous studies of  the acute upper  respiratory
           inflammatory response to a variety of  stimuli,  including antigens, cold dry air,
           ozone, and viral challenges.

     •     Respiratory and Ocular Responses -

           Normal, healthy adults will be exposed to a mixture of chemicals frequently found
           in the indoor  environment, and measures of  ventilation, pulmonary function,
           bronchial reactivity, and eye irritation as well as symptom questionnaire data will be
           obtained.  Exposure will be to two  levels of VOCs in addition to one clean air
                                          35

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           exposure in a randomized block design in which each subject serves as his own
           control.  Dependent measures will be related to the subjects' exposure burden as
           determined  from blood samples.  This laboratory experiment will identity key
           variables and provide data necessary to begin testing in near-real world exposure
           situations.  A protocol is in preparation to perform analogous experiments in EPA's
           test house in Gary, NC in which AEERL tests propagation of VOCs from household
           use products.
D.   Products:

     •     Interim report of the initial nasal lavage study

     *     Publication of analysis of pilot nasal lavage study data

     •     Objective measures of pulmonary function
           alterations in normal subjects exposed to a
           VOC mixture, an approximate dose-response relation-
           ship of a mixture of VOCs on ventilatory response

     •     Determination of whether or not subjective symptoms to
           VOC exposure are associated with multiple nerve pathways;
           characterization of the dose-response relationship
           of a mixture of VOCs on measures of odor and irritant
           intensity

     •     Interim report on the development of psychophysical
           and physiological methods to distinguish SBS responders
           from nonresponders

£.   Project Contacts:

     George Goldstein   (919) 966-6204

     Hillel Koren       (919) 966-6254
                                                        10/90

                                                        10/91

                                                        10/91
                                                         10/92
                                                        10/92
     Jim Prah

     Resources:



     FY91
 (919) 966-6244
FTE

4.0
 S&E

S248K
 R&D

S351.6K
                                         36

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PROJECT 19: TOXICOLOGICAL EFFECTS OF VOC MIXTURES IN ANIMAL AND
               JNVTTRO SYSTEMS

A.   Objective:

     To explore several aspects of the potential health impact of VOC mixtures:  1) are there
     systemic (immunological, reproductive, respiratory and/or neurobehavioral) effects resulting
     from inhalation exposures to VOC mixtures; 2) can a matrix approach to assessing VOC
     mixtures be constructed that will aid in assessing mixture toxicology due to additivity or
     interactions; 3) are these VOC mixtures more or less likely than individual VOCs to induce
     mutagenic alterations in experimental  in vitro systems?  Results  will be compared to
     information collected in human studies.
                                                   i
B.   Background:

     Offgas VOCs emitted from a  variety of construction materials and new synthetic-based
     objects (e.g., furniture) appear to affect human neurobehavior and comfort. These VOCs
     may also induce more severe health effects due to their systemic redistribution in the body
     with resultant potential impacts on reproduction, fetal development, immunology,  and
     respiratory cell function.  Some of these VOCs also appear to be cytotoxic or mutagenic
     in special  bacterial systems lending credence  to potential cytological effects,  including
     transformation (cancer). An integrated program of animal and in vitro toxicology is needed
     to pursue these research questions that are not amenable to human system study.

     Based on existing evidence of respiratory tract inflammation following  controlled VOC
     exposure,  and on complaints of increased respiratory disease as a component of the Sick
     Building Syndrome, initial  research will focus on evaluating immunotoxic effects  and
     assessing respiratory irritancy in rodents and humans (see Project 18) following controlled
     VOC exposures in inhalation chambers. Elevated ambient levels of inhaled air pollutants
     have been associated  with an increased  susceptibility to respiratory viral infections,
     particularly in children. The socioeconomic impact of influenza viral disease is estimated
     at 3-5 billion dollars per year in the United States. Viral upper respiratory tract infection
     has also been implicated as an important contributor to the etiology of asthma.  The
     incidence and mortality associated  with asthma is increasing in the United States.

C.   Approach:

     The immunotoxicity of VOC mixtures will be  assessed by measuring local pulmonary as
     well as systemic immunological functions after inhalation exposure.  Immunotoxicological
     assessment will measure the effect of VOC exposure on viral, bacterial, allergic,  and
     neoplastic diseases, as well as those immunological functions crucial to defense against these
     diseases. An influenza model of human disease will be used to assess susceptibility to upper
                                         37

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     respiratory viral infections in animals of different ages. Previous studies have shown that
     exposure to an oxidant air pollutant (ozone) enhances the airway hyperreactivity associated
     with influenza virus infection.  Studies will be performed to determine whether indoor air
     pollutant mixtures affect the susceptibility or severity of airway hyperreactivity in the
     influenza-induced model for asthma.

     Exposure to inhaled air pollutants often results in an inflammatory response as measured
     by an  increase in cellular and  mediator  biomarkers of inflammation.   Inflammatory
     responses will be measured using the same endpoints in both animal and human nasal lavage
     samples as well as bronchoalveolar lavage samples in animal. Studies observing markers
     of inflammation are expected to be sensitive and especially important because of the direct
     comparisons of animals and human exposed to VOC mixtures.

     Several additional approaches  will be used in different laboratory settings.  An  animal
     inhalation facility will be used to fulfill  experimental designs that  address simple and
     complex exposure toxicology  as well as  aim at dissecting questions of additivity or
     interaction of VOCs in a conceptual framework to develop generic approaches to  further
     mixture studies.  Inhalation facility  studies will employ a variety of systemic endpoints
     (immunological, neurobehavioral, etc.), in addition to evaluating breathing patterns as a
     measure of respiratory irritancy. Also, in collaboration with AEERL, offgas VOC initancy
     and  mutagenicity can be assessed to determine acute effects of exposure on breathing
     patterns as a bioassay system for relative potency as well as potential carcinogenicity of
     these gases or combinations. •
D.   Products:

     •     Establishment of chamber exposure capability

     •     Completion of respiratory irritancy bioassay

     •     Completion of influenza model studies

     •     Completion of respiratory inflammation biomarker tests

£.   Project Contacts:

     Dan Costa         (919) 541-2531
                        (FTS) 629-2531

     Gary Burleson      (919) 541-2555
                        (FTS) 629-2555
 10/90

10/90

10/91

10/91
                                          38

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F.  Resources:
    FY91
ECE     S&E      R&D




0.5      $31K      $190K
                                   39

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PROJECT 20:  BIOLOGICAL MARKERS FOR ENVIRONMENTAL TOBACCO SMOKE
               (ETS) EXPOSURE AND DOSIMETRY
A.   Objectives:

     Evaluate biological markers (e.g., mcotine/cotinine), that can be used effectively in
     assessing the exposure and dosimetry of ETS. Evaluate ETS using bioassay and biomarker
     methods.   Develop, evaluate,  and apply DNA  adducts and other molecular exposure
     dosimetry methods to human studies.

B.   Background:

     To provide definitive data on the relationship between human exposure, dose, and effects
     of indoor organic pollutants, it is necessary to develop markers for exposure and dosimetry.
     Personal exposure and dosimetry of ETS are dependent upon many factors such that optimal
     assessment should be measured directly through the use of biological markers of exposure,
     uptake into blood, distribution and metabolism, binding to macromolecules (e.g., protein
     and DNA), and excretion into urine.

     One approach is to identify unique tracer compounds present in ETS and their metabolites.
     Nicotine,  for example, is virtually unique to tobacco'sources and both  nicotine and its
     metabolite, cotinine, can be measured in human tissue or fluids. This approach will provide
     the  basis for relating health effects of specific exposure concentrations  and  dose.  The
     application of these markers needs to be validated in a population highly  exposed to ETS
     or in a potentially more sensitive population such as preschool children.  Cotinine has
     shown that it can be a candidate as a biochemical marker for ETS exposure. This study will
     evaluate cotinine as a marker compound for ETS exposure.  Home studies will also provide
     relevant data for real situations. These data will be compared to the chamber data to
     validate the biomarker - exposure models developed in the chamber studies.

     The carcinogenic components of ETS are thought to reside primarily in the particle phase.
     Nicotine is an ideal marker for the gaseous phase of ETS where it is present as  a free base.
     Concern that nicotine uptake by nonsmokers is not representative of the carcinogenic
     components in the particle phase led the NAS committee on ETS to recommend that other
     biomarkers be developed, particularly highly sensitive methods for measuring DNA and
     protein adducts. The 32P-postlabeling method for DNA adducts is such a method and has
     been demonstrated to be capable of detecting DNA adducts in tissues after exposure to
     tobacco smoke.
                                         40

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C.   Approach:

     A multidisciplinary approach to these studies will include evaluation of biological and
     chemical  markers  of EPS  in  controlled  chamber  studies, homes,  and in  other
     microenvironments in collaboration with AEERL and AREAL. Targeted pilot field studies
     are being undertaken collaboratively by EPA and University of North Carolina investigators
     at the Frank Porter Graham (FPG) Child Development Center.  The center is operated by
     UNC as a research day care center. There are forty children enrolled in the Center from
     an age of 3 months to 5 years.  Approximately half of the  children's  parents smoke
 ,    cigarettes. The homes of selected children enrolled in the Center are monitored for a series
 ,'    of pollutants including nicotine and paniculate mutagens.  Body fluids of these preschool
     children, both exposed and nonexposed to HIS, will be used in biological marker studies.

     Adults and young children from homes where tobacco smoke is present will be exposed to
     known concentrations of EPS in an environmentally controlled chamber.  Urine will be
     collected from subjects, prior to exposure and up to several days postexposure.  Urine
     cotinine excretion  rates will be determined  and correlated to air  nicotine  exposure.
     Validation studies will be conducted in adults using deuterated nicotine to quantitate the
     relationship between exposure uptake and elimination.  The dose of nicotine.will be varied
     by changing the number of cigarettes smoked during the exposure  in order to give a dose
     response.  The excretion of cotinine will be correlated with the dose of nicotine as well as
     age, sex, and race in the infant/child population.  This information is considered critical
     because it will allow one to estimate prior exposure, with a high degree of certainty,  rather
     than rely on questionnaire data.  This study is to determine the exposure dose of nicotine,
     the peak level of urinary cotinine,  the time to peak levels  of cotinine,  and  the elimination
     half-life of urinary cotinine when children are exposed to a  controlled amount of ETS. This
     work will support the use of cotinine as a biomarker in the planned NUi study of the effects
     of ETS on children. The performance of cotinine as a biomarker will be further evaluated
     in this study.   ;

     We have developed methods to detect DNA adducts  in human cells and tissues as a result
     of exposures  to  complex  mixtures.   The  use of DNA adducts  as  determined by
     32P-postlabeling and enzyme linked immunosorbent assay (ELISA) is being developed as
     a molecular biomarker of exposure to tobacco smoke.  Lung cells from bronchoalveolar
     lavage of humans  in  clinical studies  have provided evidence  that smoking adducts are
     detectable. Expanded human study research using a larger number of individuals will be
     conducted.
                                          41

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D.   Products:

     •     Assessment of preschool children's exposure to ETS using
           nicotine, particle-phase mutagens, and cotinine

     •     Establishment of relationship between personal exposure to
           nicotine and other pollutants (e.g., mutagens,  RSP) and
           cotinine

     •     Determination of elimination half-life of cotinine in young
           children exposed to different dose levels of ETS

     •     Evaluation of ETS dosimetry in humans using DNA adducts

£.   Project Contact:

      Joellen Lewtas     (919) 541-3849
                       (FTS) 629-3849
                                                         1/91


                                                        10/91



                                                         5/92


                                                        11/93
F.   Resources:
     FY91
FTE     S&E       R&D

0.5      $31K      $300K*
                                         42

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BIOCONTAMINATION ASSESSMENT

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PROJECT 21: ASSESSMENTS OF MICROBIOLOGICAL PROGRAM HAZARDS IN
               THE INDOOR AIR ENVIRONMENT
A.   Objectives:

     Modify existing methods or develop new methods to capture and detect air-borne microbes.
     Develop innovative methods to characterize potentially hazardous microbes and microbial
     products  in the indoor environment. Evaluate newly developed methods under actual
     environmental conditions. Develop indoor-air quality criteria for pathogens and allergens.

B.   Background:

     Microbiological contaminants in the indoor air environment may pose significant health
     risks to exposed individuals.  The risks are presented by three types of microbiological
     exposure factors:  pathogens, allergens, and toxins.  Examples of these exposure factors
     include:  1) Legionella pneumophila and Aspergillus fianigatus pathogens, which cause
     Legionnaires Disease, and severe respiratory disease, respectively; 2) Penicillium species
     and Bacillus  subtilis,  airborne  allergens  that  are capable of  causing life threatening
     hypersensitivity pneumonitis; and 3) Aspergillus flavus and gram negative bacteria that
     produce,  respectively, aflatoxins and endotoxins, both of which are hazardous to the health
     of humans. The indoor air microbiological research issues associated with these microbes
     and microbial products fall into three major categories.  First, the need for standardized
     microbiological methods; second, the need to define the relationship between indoor air
     quality and infections or allergies; and third, the need to characterize sources of indoor air
     contaminants.

C.   Approach:

     A key element of the indoor air microbiology program is to examine the concept of critical
     factors in assessing exposure.  Critical factors are characteristics that determine whether or
     not microbes or their products pose a health risk to humans. This approach requires not
     only that bacteriological or fungal growth media detect as broad a range of bacteria or fungi
     as possible, but also that the detection rate should be at maximum.  These features will be
     accomplished by identifying the stresses and injuries suffered by airborne microbes and then
     developing appropriate media to resuscitate the organisms and optimize their growth.
                                          43

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Two critical factors exhibited by airborne microbes are pathogenicity and allergenicity. The
former is associated with respiratory infection and disease and the latter is associated with
a wide  variety of allergic responses.  The critical factors for pathogens are virulence
determinants and for allergens they are antigens that react with certain immunoglobulins
associated with specialized lymphocytes.  Facile, specific in vitro tests will be developed
to detect and quantify these critical factors.

Although critical factors can be used to establish meaningful relationships between exposure
and resulting effects, it is frequently necessary to identify potential pathogens or allergen
producing microbes, such as fungi. Bacteria are easily identified using biochemical and
serological tests, but fungi are very difficult to identify. Identification usually requires a
highly skilled individual  whose expertise has been developed  over many years.  In order
to replace the need for a highly skilled person a series of gene probes will be developed for
those fungi commonly found in indoor environments.  This approach will allow a less
highly skilled person to identify important fungal species easily and rapidly.

Once the methods for capturing and detecting potentially hazardous microbes have been
completed and the means to characterize and identify the organisms developed, the system
will be evaluated under field conditions  (i.e., in the indoor environment). This will be done
by identifying  various types of indoor microbial exposures, sampling  the  air in those
environments, and characterizing and quantifying the exposure factors.  During this period
the exposure assessment methods will be standardized and quality assurance protocols will
be developed.                                                         .

The final phases of the  microbiology  indoor air program will examine  the relationship
between the  exposure factor assessments and the rate of response observed in  humans
exposed to various levels of the exposure factors. This information will be used to develop
air quality criteria for indoor environments.
Products:
       A standard collection fluid for impinger samplers

       A standard method for detecting total bacteria

       A standard method for detecting total fungi

       Report on field evaluation of the standard fluid &
       methods developed above

       Report describing the relationship between illness or
       allergies and indoor air quality.
 9/93

 9/93

 9/93

 9/94


9/96
                                      44

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£.  Contact:
    Alfred Dufour    (513) 569-7218
                    (FTS) 684-7218
F.  Resources:


    FY91
FTE    S&E

3        —
 R&D

$600K*
    *$200K to be transferred from TEAM program
    *$200K to be transferred from other programs
                                     45

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PROJECT 22: MODELING AND MONITORING DESIGN FOR THE RETRIEVAL OF
               MICROORGANISMS IN INDOOR AIR ENVIRONMENTS
A.   Objectives:

     To construct an experimental room resembling a residential indoor air environment with
     controllable temperature and relative humidity, air flows, and exchange rates. Determine
     the optimal aerobiological sampling for retrieval of fungal spores in an experimental room
     resembling an indoor air setting.  Evaluate surfaces from microbial loading resulting from
     input from an air handling system and the effect of human activity on the concentration of
     airborne  spores.  Determine the  efficacy .of chemical-based surface contact biocide
     antimicrobial intervention  technique on reducing  the load  of fungus  in  the  indoor
     environment. Determine if construction materials used in the ductwork of an air handling
     system result in significant differences in the contamination of an indoor air environment
     by that air-handling system.  Increase the data base of information on the effect of human
     activity within the room on the concentration of airborne spores.  Validate previously
     obtained  data on the efficacy of a chemical-based surface contact biocide antimicrobial
     intervention  technique to reduce the  fungal load in an indoor environment and provide
     information on the impact of microorganisms and their metabolites on indoor air quality.

B.   Background:                    .

     The dissemination of microbial contaminants  within  the indoor air environment by
     heating/cooling systems or the growth and dispersal of microbial agents from individual
     room  sources  may  significantly contribute to  "building  related  illness."  Insufficient
     information, however, is available on the dispersal of airborne microorganisms indoors or
     optimal monitoring designs for their detection.  To date, there is insufficient information
     on the relative efficiency of aerobiological sampling equipment operating in indoor air
     environments for the retrieval of bacteria and fungi to design valid indoor air monitoring
     protocols. Side-by-side comparisons of some of the commonly used samplers will provide
     a basis for selecting  sampling methods appropriate for retrieval of airborne cells.

     There is also insufficient information on the contribution of human activity  to the numbers
     of airborne microorganisms disseminated within indoor air environments. This information
     is necessary to understand data being collected during indoor air surveys. An antimicrobial
     surface contact biocide (Sylgard   , Dow Corning Corporation, Midland, MI)  has been
     shown to reduce complaints of sick building syndrome following treatment of walls, carpet,
     and ceiling materials. Data will verify the efficacy of this product on the concentration of
     fungi in a heavily contaminated indoor air environment and correlate information on the
     utility of retrieval techniques in demonstrating this efficacy.
                                         46

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     Materials used in the construction of air handling system ductwork may contribute to the
     growth and dissemination of biological contaminates in indoor air environments.  The
     introduction of fungal spores through ductwork composed of different materials would be
     feasible in a room environment described in Phase I of this project.   Comparisons could
     then be made on the contribution of the ductwork construction material to total particle
     counts, loading of the room with contaminant microorganisms, and intervention.

     Mixed microbial populations and the metabolic by-products of microbial growth  may
     significantly contribute to "building related illness." Insufficient data, however, have been
     collected under controlled  conditions to fully assess these  factors.   Characterizing,
     identifying, and quantifying of mixed populations of organisms and the volatile metabolites
     resulting from microbial contamination and growth within a model room would significantly
     increase the information available on indoor air quality.  Additionally,  the development of
     nonculture based measurement and monitoring methods could provide enhanced detection
     methods for use in indoor air investigations.

C.   Approach:

     A room (15  ft x 15 ft x~8 ft) will be constructed  within the confines of a greenhouse at
     EMSL-LV.  The room will be  constructed  with galvanized ductwork and a HVAC air
     handling system housed in the greenhouse bay.  Air exchange and ventilation rates will be
     controlled by shunting off the excess air through the greenhouse bay to the outside. It will
     resemble a residential room with two passageway doors, sheetrock walls and ceilings, and
     a carpeted floor.  An anteroom will be attached to each of the two passageways to provide
     a place to don  protective clothing and to reduce mixing of air resulting from entering and
     exiting of the room during experiments.

     The room will be characterized as a pretest prior to the introduction of microorganisms.
     This pretest will include retrieval of airborne particles for characterization by the Thermal
     Insulation Manufacturer's Association.  Laboratory-based microbiology experiments will
     be conducted on the target fungus and the project quality assurance plan will be written.

     At the completion of this stage,  an experimental room will be available to the microbial
     studies group for ongoing research activities on airborne microorganisms. The room will
     provide a controlled environmental system for long-term dynamic studies with various
     materials,  heating system  components, ventilation rates, temperature and humidity,
     microbial populations, and volatile microbial metabolites.

     Total  particle counts of material resulting from the ductwork  and HVAC system will be
     recorded to provide background information on the contribution to total particulates in
     indoor air from the galvanized ductwork.
                                          47

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       D.  Products:
       E.  Project Contact:

           Stephen C. Hern   (702) 798-2100
                            (FTS) 545-2100
.
F.  Resources:


    FY91
                           FTE     S&E
R&D
                                             48
.

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