-------
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.
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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.
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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.
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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.
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Osborne, M. C. et al. (1988) Radon reduction in an crawl space house. J. Environ. Engineering 115(3):
589.
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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,
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
-------
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.
-------
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
-------
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
-------
^OGRAMroR
1990' ":*=^r-; •;••;•>:£
-------
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.
-------
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.
-------
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.
-------
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
-------
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.
-------
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.
-------
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
-------
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
-------
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
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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
-------
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
-------
£. Project Contact:
Michael A. Berry (919)541-4172
(FTS) 629-4172
F. Resources:
FY91
FTE S&E R&D
0.25 $25K $25K
8
-------
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
-------
INDOOR AIR SOURCE CHARACTERIZATION
AND MITIGATION
-------
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
-------
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
-------
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
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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
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F. Resources:
FY91
ECE S&E R&D
0.5 $31K $190K
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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.
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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.
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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*
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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.
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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
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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
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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.
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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.
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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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