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Indoor Air Pollution
Sara Lance
Kim Kubera
Arsineh Hecobian
Rick Peltier
Introduction and Summary
 Sources of Indoor Air Pollutants
 Transportation/Movement
 Unique Chemistry
 Specific Health Effects
Indoor Air Pollution - Overview
 People spend most of their time indoors.
 The EPA has shown that indoor levels of some
pollutants, such as formaldehyde, chloroform,
and styrene, range from 2 to 50 times higher
than outdoor levels.
 Exposure to pollutants such as environmental
tobacco smoke and radon occurs almost
entirely indoors.
Indoor Air Pollution
 Main Categories:
1) toxic gases
e.g. carbon monoxide, ozone, formaldehyde
2) particulate matter
e.g. candles, incense, smoke, pet dander
3) radiogenic species
e.g. Radon-220, Polonium-210
4) biological organisms
e.g. mold, dust mites, bacteria
Some Specific Indoor Air Pollutants
 Acetone - in cosmetics, fragrances, human breath
 Ammonia - in cleaning products
 Benzene - in laser printers, particle board, paint, tobacco
 Benzaldehyde - in detergents and fragrances
 Benzyl acetate - in air fresheners, fragrances
 Chloroform - in chlorinated tap water
 Formaldehyde - in particle boards, carpets, clothes, glue
 Limonene - in deodorants, disinfectants, fragrances
 Terpinen - in deodorants, fragrances
 Toulene - in glue, laser printers, paint and particle board
 Trichloroethyl - in photocopiers
 Xylene - in glue, laser printers, paint and particle board
 Laser printers
 Photocopiers
 Fax machines
 Ozone Generators
 touted as “Air Cleaning” devices
Indoor Sources of Ozone
EPA’s Stance on Ozone
Generators
 ozone generators are not effective at removing
many of the most harmful chemicals--including
carbon monoxide and formaldehyde--commonly
found in indoor environments.
 for many of the chemicals with which ozone does
readily react, ozone forms a variety of harmful or
irritating by-products, including aldehydes and
other organic chemicals.
 ozone does not remove particles (such as dust and
pollen) from the air.
Coverage - up to 2,000 square feet
Maximum Ozone Output - 750 mg/hr
Ozone Generator - http://www.purennatural.com
The “Ozone Zapper”- According to Specs
 With “perfect mixing”, the maximum output
rate (750 mg/hr) combined with the maximum
area coverage (2,000 ft2) gives an ozone
production rate of 920 ppb/hr.
 Ozone concentrations will be greater near the
“Ozone Zapper” source.
 920 ppb O3 is more than 10 times the EPA’s
eight-hour standard.
Lead Particulates - Candle Burning
 The core of candle wicks may contain lead.
 Out of the molten wax, lead can be emitted as
particulate to the air.
 In an EPA study, of 100 sets of candles that
appeared to have metal-core wicks, 8%
contained lead wicks.
Environmental Tobacco Smoke (ETS)
 The EPA has classified environmental
tobacco smoke as a class A carcinogen,
responsible for approximately 3,000
lung cancer deaths and 62,000 heart
disease deaths annually in U.S. non-
smokers.
 ETS includes toxic gases, particulate
matter and radiogenic species.
Among the powerful poisons in
Environmental Tobacco Smoke (ETS) are:
 Carbon monoxide
 Nitrogen oxide
 Ammonia
 Methyl isocyanate
 Hydrogen cyanide
 Phenol
 Among the carcinogens in ETS are:
 Benzo [a] pyrene
 Nitrosamines
 Aromatic amines
 Benzene
 Formaldehyde
 Polonium-210 (radioactive)
Tobacco Toxins
Radon
 A colorless, odorless, invisible radioactive gas,
is released into the air from the uranium found
naturally in rocks and soil.
Radon Entry Points – US EPA
Radon Exposure – EPA Guidelines
 EPA Standard for Radon = 4 pCi/L
 Out of 1,000 people exposed to 4 pCi/L over a
lifetime, 2 non-smokers and 29 smokers are
predicted to get lung cancer.
 Smoking and radon gas exposure show a
synergistic relationship with respect to lung
cancer.
Estimated Fraction of Homes with Long-term, Living-
Area Average Radon Concentrations over 4 pCi/L
Legionnaires’ Disease
 “A bacterial disease commonly
associated with water-based
aerosols and often a result of
poorly maintained air
conditioning cooling towers
and potable water systems.”
(OSHA)
 Cases have been reported in
the US, Australia, Netherlands,
UK…
Dust Mites
These microscopic insects excrete
proteins that can trigger asthma
and allergy attacks in people.
“Typical places to find
mites are the mattress, and
the carpeting next to the
bed, because the bed is
where we spend the
majority of our time -- at
least 8 hours a day
sleeping, so we lose a lot of
skin cells there,” said Glass.
“The average person sheds
enough skin cells every day
to feed thousands of mites
for a month.”
Indoor Pollution Transport
 Indoor to Outdoor, Outdoor to Indoor
Transport (basic methods/terminology)
 How do you improve indoor air pollution
Basic Transportation
 Infiltration
- flows into the house through
openings, joints, and cracks in walls,
floors, and ceilings, and around windows
and doors.
 Natural ventilation
- air moves through opened
windows and doors.
(Air movement associated with
infiltration and natural ventilation is
caused by air temperature
differences between indoors and
outdoors and by wind.)
Transport - Continued
 Mechanical ventilation
- 1.outdoor-vented fans that
intermittently remove air from a single
room
- 2. air handling systems that use
fans and duct work to continuously
remove indoor air and distribute filtered
and conditioned outdoor air to strategic
points throughout the house.
 The rate at which outdoor air replaces
indoor air is described as the air
exchange rate. When there is little
infiltration, natural ventilation, or
mechanical ventilation, the air
exchange rate is low and pollutant
levels can increase.
Source Control
 eliminate individual sources of pollution or to
reduce their emissions.
- seal or enclose (asbestos)
- adjust to decrease the amount of
emissions.
(gas stoves)
 In many cases, source control is also a more
cost-efficient approach to protecting indoor air
quality than increasing ventilation because
increasing ventilation can increase energy
costs.
Ventilation Improvements
 increase the amount of outdoor air
coming indoors.
- Opening windows and doors,
operating window or attic fans, when the
weather permits, or running a window air
conditioner with the vent control open
increases the outdoor ventilation rate.
Ventilation - Continued
 important to take as many of these
steps as possible while you are involved
in short-term activities that can generate
high levels of pollutants.
- painting, paint stripping, heating
with kerosene heaters, cooking, or
engaging in maintenance and hobby
activities such as welding, soldering, or
sanding.
Air Cleaners
 many types and sizes of air cleaners on the
market
- ranging from relatively inexpensive table-
top models to sophisticated and expensive
whole-house systems.
 Some are highly effective at particle removal,
while others, including most table-top models,
are much less so.
 Air cleaners are generally not designed to
remove gaseous pollutants.
Air Cleaners - Continued
 The effectiveness of an air cleaner depends
on how well it collects pollutants from indoor
air and how much air it draws through the
cleaning or filtering element.
 A very efficient collector with a low air-
circulation rate will not be effective, nor will a
cleaner with a high air-circulation rate but a
less efficient collector.
 The long-term performance of any air cleaner
depends on maintaining it according to the
manufacturer's directions.
 Another important factor in determining
the effectiveness of an air cleaner is the
strength of the pollutant source.
 Table-top air cleaners may not remove
satisfactory amounts of pollutants from
strong nearby sources.
Indoor Chemical Pollutants
 Sources (physical and chemical)
 Sinks (physical and chemical)
 Reactions (chemical sources and sinks)
Some Chemical Air Pollutants
 Sulfur Dioxide
 Carbon Monoxide
 Nitrogen Dioxide
 Particulate Matter
 Ozone
Some Volatile Organic Compounds
Compound Health Effects
Benzene Carcinogen; respiratory tract irritant
Xylenes Narcotic; irritant; affects heart, liver, kidney, and
nervous system
Toluene Narcotic; possible cause of anemia
Styrene Narcotic; affects control of nervous system; probable
human carcinogen
Toluene diisocyanate (TDI) Sensitizer; probable human carcinogen
Trichlaroethane Affects central nervous system
Ethyl benzene Severe irritation of eyes and respiratory tract; affects
central nervous system
Dichloromethane Narcotic; affects nervous system; probable human
carcinogen
1.4-Dichlorobenzene Narcotic; affect liver, kidney, and central nervous
system; eye and respiratory tract irritant
Benzyl chloride Central nervous system depressant; affects liver and
kidney; eye and respiratory tract irritant
2-Butanone (MEK) Irritant; central nervous system depressant
Petroleum distillates Affects central nervous system, liver, and kidneys
4-Phenylcyclohexene Eye and respiratory tract irritant; central nervous
system
Source: U.S. Environmental Protection Agency (EPA). Introduction to Indoor Air Quality. Report no. EPA/400/3–91/ 003, Washington, DC: U.S.
Environmental Protection Agency, 1991.
Reaction between -pinene and O3
Source: The significance of secondary organic aerosol formation and growth in buildings: experimental and computational evidence
Golam Sarwar, Richard Corsi, David Allen and Charles Weschler
What Chemicals are
IMPORTANT?
 Free Radicals (OH)
 Oxidizers (O3)
NOx
 Sources
 Transport
 Combustion Processes
 Range:
 Indoor: 20-50 ppb
 Outdoor: 10-500 ppt (Ludwig et al, 1974)
 O3+NO NO2+O2
The importance of NOx
 O3+NO2 NO3+O2
 NO3+RH HNO3+Ro
OH Radical
 Outdoor to indoor transport
 Reactions with VOC
Calculated rate constants for removal of hydroxyl radical
Source: Free radical chemistry and its concern with indoor air quality: an open problem, Giovanni Ingrosso
Source:Indoor Chemistry: Ozone and Volatile Organic Compounds Found in Tobacco Smoke Richard J. Shaughnessy, T. J.
McDaniels, and Charles J. Weschler
Tobacco Smoke: Inert Chemicals
Source:Indoor Chemistry: Ozone and Volatile Organic Compounds Found in Tobacco Smoke Richard J. Shaughnessy, T. J.
McDaniels, and Charles J. Weschler
Tobacco Smoke: Reactive Chemicals
Source:Indoor Chemistry: Ozone and Volatile Organic Compounds Found in Tobacco Smoke Richard J. Shaughnessy, T. J.
McDaniels, and Charles J. Weschler
Chemicals Produced From Ozone Reactions
Surface Deposition
 More surface areas
 Different types of surfaces
 Relative Humidity
The Bigger Picture: Impacts on
Humanity
 Americans spend majority of their
day in an indoor environment.
 Other cultures can spend more/less
time indoors
Health Effects - Respiratory
Physiology affords a
uniquely reactive
environment
Direct pathways to
internal systems
Although low in tidal
volume, high in
frequency (69000
liter/day = 6900 m3/day
(= 13.2 kilogram at PM10
standard of 75mg over
lifetime)
Health Effects - Cardiac
 Peters et al. – strong
correlation between
ST segment
elevation and PM2.5
mass.
 Acid deposition (gas
and particle) and
linkage to cardiac
ischemia???
Biogenic Air Pollutants
 Chew et al. – Cockroach allergen and
sensitivity to Asthma
 Consistent 8-10 hour exposure to
Epidermal detritus
 Pet dander
Adequacy of Monitoring
 Debatable whether or
not EPA monitors reflect
magnitude of exposures
– monitors generally
deployed near industrial
facilities to monitor
compliance.
 Personal monitors
currently best way to
measure exposure
(although far from
perfect – “personal
cloud”)
The Comforts of Home
 Tolerance for ETS
 Pesticide/herbicide application
 Cooking
 “workshop” products
A Special Health Concern:
 Children
 Curiosity
 Developing
 High
metabolism
 Ground-level
activity
Non-Health Effects
 Stress  decreased job performance,
missed time at work/school, etc.
 Oxidants  decaying possessions (i.e.
artwork, food products)

Summary and Conclusions
 Sources
 Heterogeneous, numerous, etc.
 Transport
 Not uniform throughout homes, critical to
understanding chemistry
 Chemistry
 Both oxidizing and reducing environments, wider
array of chemical species
 Effects
 Health and other effects widespread, largely due
to “comforts of home”.
Bibliography
Burge, H. Bioaerosols: Prevalence and Health Effects in the Indoor Environment. J Allergy and Clin
Immunology: 86:5, 687-702, 1990.
Clean Air Amendments of 1970, Public Law 91–604, 84 Statute, December 31,1970. Air Standards
Authorization implemented by U.S. Environmental Protection Agency, Washington, DC, April 30, 1971.
Chew G; Stelmach I; Jerzynska J; Stelmach W; Majak P; Gorski P; Kuna Cockroach allergy and exposure to
cockroach allergen in Polish children with Asthma. Allergy, 2002 Aug, 57(8):701-5
Munir, A., Kjellman, M., Bjorksten, B. Exposure to Indoor Allergens in Early Infancy and Senstization. J
Allergy and Clin Immunology. 100:2, 177-181, 1997.
Peters, A., D. Dockery, et al. (2001). "Increased Particulate Air Pollution and the Triggering of Myocardial
Infarction." Circulation 103: 2810-2815.
Ritchie, Ingrid.; Martin, Stephen John. The Healthy Home Kit : Inspecting for Environmental Hazards, Working
With Professionals to Avoid Risks, Cleaning Up Radon, Lead, Asbestos, and More!
U.S. Environmental Protection Agency (EPA). Introduction to Indoor Air Quality. Report no. EPA/400/3–91/
003, Washington, DC: U.S. Environmental Protection Agency, 1991.
U.S. Environmental Protection Agency, Indoor Air Pollution: An Introduction for Health Professionals, No. 1994-
523-217/81322, 1994

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Indoor.ppt

  • 1. Indoor Air Pollution Sara Lance Kim Kubera Arsineh Hecobian Rick Peltier
  • 2. Introduction and Summary  Sources of Indoor Air Pollutants  Transportation/Movement  Unique Chemistry  Specific Health Effects
  • 3. Indoor Air Pollution - Overview  People spend most of their time indoors.  The EPA has shown that indoor levels of some pollutants, such as formaldehyde, chloroform, and styrene, range from 2 to 50 times higher than outdoor levels.  Exposure to pollutants such as environmental tobacco smoke and radon occurs almost entirely indoors.
  • 4. Indoor Air Pollution  Main Categories: 1) toxic gases e.g. carbon monoxide, ozone, formaldehyde 2) particulate matter e.g. candles, incense, smoke, pet dander 3) radiogenic species e.g. Radon-220, Polonium-210 4) biological organisms e.g. mold, dust mites, bacteria
  • 5. Some Specific Indoor Air Pollutants  Acetone - in cosmetics, fragrances, human breath  Ammonia - in cleaning products  Benzene - in laser printers, particle board, paint, tobacco  Benzaldehyde - in detergents and fragrances  Benzyl acetate - in air fresheners, fragrances  Chloroform - in chlorinated tap water  Formaldehyde - in particle boards, carpets, clothes, glue  Limonene - in deodorants, disinfectants, fragrances  Terpinen - in deodorants, fragrances  Toulene - in glue, laser printers, paint and particle board  Trichloroethyl - in photocopiers  Xylene - in glue, laser printers, paint and particle board
  • 6.  Laser printers  Photocopiers  Fax machines  Ozone Generators  touted as “Air Cleaning” devices Indoor Sources of Ozone
  • 7. EPA’s Stance on Ozone Generators  ozone generators are not effective at removing many of the most harmful chemicals--including carbon monoxide and formaldehyde--commonly found in indoor environments.  for many of the chemicals with which ozone does readily react, ozone forms a variety of harmful or irritating by-products, including aldehydes and other organic chemicals.  ozone does not remove particles (such as dust and pollen) from the air.
  • 8. Coverage - up to 2,000 square feet Maximum Ozone Output - 750 mg/hr Ozone Generator - http://www.purennatural.com
  • 9. The “Ozone Zapper”- According to Specs  With “perfect mixing”, the maximum output rate (750 mg/hr) combined with the maximum area coverage (2,000 ft2) gives an ozone production rate of 920 ppb/hr.  Ozone concentrations will be greater near the “Ozone Zapper” source.  920 ppb O3 is more than 10 times the EPA’s eight-hour standard.
  • 10. Lead Particulates - Candle Burning  The core of candle wicks may contain lead.  Out of the molten wax, lead can be emitted as particulate to the air.  In an EPA study, of 100 sets of candles that appeared to have metal-core wicks, 8% contained lead wicks.
  • 11. Environmental Tobacco Smoke (ETS)  The EPA has classified environmental tobacco smoke as a class A carcinogen, responsible for approximately 3,000 lung cancer deaths and 62,000 heart disease deaths annually in U.S. non- smokers.  ETS includes toxic gases, particulate matter and radiogenic species.
  • 12. Among the powerful poisons in Environmental Tobacco Smoke (ETS) are:  Carbon monoxide  Nitrogen oxide  Ammonia  Methyl isocyanate  Hydrogen cyanide  Phenol  Among the carcinogens in ETS are:  Benzo [a] pyrene  Nitrosamines  Aromatic amines  Benzene  Formaldehyde  Polonium-210 (radioactive) Tobacco Toxins
  • 13. Radon  A colorless, odorless, invisible radioactive gas, is released into the air from the uranium found naturally in rocks and soil.
  • 14. Radon Entry Points – US EPA
  • 15. Radon Exposure – EPA Guidelines  EPA Standard for Radon = 4 pCi/L  Out of 1,000 people exposed to 4 pCi/L over a lifetime, 2 non-smokers and 29 smokers are predicted to get lung cancer.  Smoking and radon gas exposure show a synergistic relationship with respect to lung cancer.
  • 16. Estimated Fraction of Homes with Long-term, Living- Area Average Radon Concentrations over 4 pCi/L
  • 17. Legionnaires’ Disease  “A bacterial disease commonly associated with water-based aerosols and often a result of poorly maintained air conditioning cooling towers and potable water systems.” (OSHA)  Cases have been reported in the US, Australia, Netherlands, UK…
  • 18. Dust Mites These microscopic insects excrete proteins that can trigger asthma and allergy attacks in people. “Typical places to find mites are the mattress, and the carpeting next to the bed, because the bed is where we spend the majority of our time -- at least 8 hours a day sleeping, so we lose a lot of skin cells there,” said Glass. “The average person sheds enough skin cells every day to feed thousands of mites for a month.”
  • 19.
  • 20. Indoor Pollution Transport  Indoor to Outdoor, Outdoor to Indoor Transport (basic methods/terminology)  How do you improve indoor air pollution
  • 21. Basic Transportation  Infiltration - flows into the house through openings, joints, and cracks in walls, floors, and ceilings, and around windows and doors.
  • 22.  Natural ventilation - air moves through opened windows and doors. (Air movement associated with infiltration and natural ventilation is caused by air temperature differences between indoors and outdoors and by wind.) Transport - Continued
  • 23.  Mechanical ventilation - 1.outdoor-vented fans that intermittently remove air from a single room - 2. air handling systems that use fans and duct work to continuously remove indoor air and distribute filtered and conditioned outdoor air to strategic points throughout the house.
  • 24.  The rate at which outdoor air replaces indoor air is described as the air exchange rate. When there is little infiltration, natural ventilation, or mechanical ventilation, the air exchange rate is low and pollutant levels can increase.
  • 25.
  • 26. Source Control  eliminate individual sources of pollution or to reduce their emissions. - seal or enclose (asbestos) - adjust to decrease the amount of emissions. (gas stoves)  In many cases, source control is also a more cost-efficient approach to protecting indoor air quality than increasing ventilation because increasing ventilation can increase energy costs.
  • 27. Ventilation Improvements  increase the amount of outdoor air coming indoors. - Opening windows and doors, operating window or attic fans, when the weather permits, or running a window air conditioner with the vent control open increases the outdoor ventilation rate.
  • 28. Ventilation - Continued  important to take as many of these steps as possible while you are involved in short-term activities that can generate high levels of pollutants. - painting, paint stripping, heating with kerosene heaters, cooking, or engaging in maintenance and hobby activities such as welding, soldering, or sanding.
  • 29. Air Cleaners  many types and sizes of air cleaners on the market - ranging from relatively inexpensive table- top models to sophisticated and expensive whole-house systems.  Some are highly effective at particle removal, while others, including most table-top models, are much less so.  Air cleaners are generally not designed to remove gaseous pollutants.
  • 30. Air Cleaners - Continued  The effectiveness of an air cleaner depends on how well it collects pollutants from indoor air and how much air it draws through the cleaning or filtering element.  A very efficient collector with a low air- circulation rate will not be effective, nor will a cleaner with a high air-circulation rate but a less efficient collector.  The long-term performance of any air cleaner depends on maintaining it according to the manufacturer's directions.
  • 31.  Another important factor in determining the effectiveness of an air cleaner is the strength of the pollutant source.  Table-top air cleaners may not remove satisfactory amounts of pollutants from strong nearby sources.
  • 32.
  • 33. Indoor Chemical Pollutants  Sources (physical and chemical)  Sinks (physical and chemical)  Reactions (chemical sources and sinks)
  • 34. Some Chemical Air Pollutants  Sulfur Dioxide  Carbon Monoxide  Nitrogen Dioxide  Particulate Matter  Ozone
  • 35. Some Volatile Organic Compounds Compound Health Effects Benzene Carcinogen; respiratory tract irritant Xylenes Narcotic; irritant; affects heart, liver, kidney, and nervous system Toluene Narcotic; possible cause of anemia Styrene Narcotic; affects control of nervous system; probable human carcinogen Toluene diisocyanate (TDI) Sensitizer; probable human carcinogen Trichlaroethane Affects central nervous system Ethyl benzene Severe irritation of eyes and respiratory tract; affects central nervous system Dichloromethane Narcotic; affects nervous system; probable human carcinogen 1.4-Dichlorobenzene Narcotic; affect liver, kidney, and central nervous system; eye and respiratory tract irritant Benzyl chloride Central nervous system depressant; affects liver and kidney; eye and respiratory tract irritant 2-Butanone (MEK) Irritant; central nervous system depressant Petroleum distillates Affects central nervous system, liver, and kidneys 4-Phenylcyclohexene Eye and respiratory tract irritant; central nervous system Source: U.S. Environmental Protection Agency (EPA). Introduction to Indoor Air Quality. Report no. EPA/400/3–91/ 003, Washington, DC: U.S. Environmental Protection Agency, 1991.
  • 36. Reaction between -pinene and O3 Source: The significance of secondary organic aerosol formation and growth in buildings: experimental and computational evidence Golam Sarwar, Richard Corsi, David Allen and Charles Weschler
  • 37. What Chemicals are IMPORTANT?  Free Radicals (OH)  Oxidizers (O3)
  • 38. NOx  Sources  Transport  Combustion Processes  Range:  Indoor: 20-50 ppb  Outdoor: 10-500 ppt (Ludwig et al, 1974)  O3+NO NO2+O2
  • 39. The importance of NOx  O3+NO2 NO3+O2  NO3+RH HNO3+Ro
  • 40. OH Radical  Outdoor to indoor transport  Reactions with VOC
  • 41. Calculated rate constants for removal of hydroxyl radical Source: Free radical chemistry and its concern with indoor air quality: an open problem, Giovanni Ingrosso
  • 42. Source:Indoor Chemistry: Ozone and Volatile Organic Compounds Found in Tobacco Smoke Richard J. Shaughnessy, T. J. McDaniels, and Charles J. Weschler Tobacco Smoke: Inert Chemicals
  • 43. Source:Indoor Chemistry: Ozone and Volatile Organic Compounds Found in Tobacco Smoke Richard J. Shaughnessy, T. J. McDaniels, and Charles J. Weschler Tobacco Smoke: Reactive Chemicals
  • 44. Source:Indoor Chemistry: Ozone and Volatile Organic Compounds Found in Tobacco Smoke Richard J. Shaughnessy, T. J. McDaniels, and Charles J. Weschler Chemicals Produced From Ozone Reactions
  • 45. Surface Deposition  More surface areas  Different types of surfaces  Relative Humidity
  • 46.
  • 47. The Bigger Picture: Impacts on Humanity  Americans spend majority of their day in an indoor environment.  Other cultures can spend more/less time indoors
  • 48. Health Effects - Respiratory Physiology affords a uniquely reactive environment Direct pathways to internal systems Although low in tidal volume, high in frequency (69000 liter/day = 6900 m3/day (= 13.2 kilogram at PM10 standard of 75mg over lifetime)
  • 49. Health Effects - Cardiac  Peters et al. – strong correlation between ST segment elevation and PM2.5 mass.  Acid deposition (gas and particle) and linkage to cardiac ischemia???
  • 50. Biogenic Air Pollutants  Chew et al. – Cockroach allergen and sensitivity to Asthma  Consistent 8-10 hour exposure to Epidermal detritus  Pet dander
  • 51. Adequacy of Monitoring  Debatable whether or not EPA monitors reflect magnitude of exposures – monitors generally deployed near industrial facilities to monitor compliance.  Personal monitors currently best way to measure exposure (although far from perfect – “personal cloud”)
  • 52. The Comforts of Home  Tolerance for ETS  Pesticide/herbicide application  Cooking  “workshop” products
  • 53. A Special Health Concern:  Children  Curiosity  Developing  High metabolism  Ground-level activity
  • 54. Non-Health Effects  Stress  decreased job performance, missed time at work/school, etc.  Oxidants  decaying possessions (i.e. artwork, food products) 
  • 55. Summary and Conclusions  Sources  Heterogeneous, numerous, etc.  Transport  Not uniform throughout homes, critical to understanding chemistry  Chemistry  Both oxidizing and reducing environments, wider array of chemical species  Effects  Health and other effects widespread, largely due to “comforts of home”.
  • 56. Bibliography Burge, H. Bioaerosols: Prevalence and Health Effects in the Indoor Environment. J Allergy and Clin Immunology: 86:5, 687-702, 1990. Clean Air Amendments of 1970, Public Law 91–604, 84 Statute, December 31,1970. Air Standards Authorization implemented by U.S. Environmental Protection Agency, Washington, DC, April 30, 1971. Chew G; Stelmach I; Jerzynska J; Stelmach W; Majak P; Gorski P; Kuna Cockroach allergy and exposure to cockroach allergen in Polish children with Asthma. Allergy, 2002 Aug, 57(8):701-5 Munir, A., Kjellman, M., Bjorksten, B. Exposure to Indoor Allergens in Early Infancy and Senstization. J Allergy and Clin Immunology. 100:2, 177-181, 1997. Peters, A., D. Dockery, et al. (2001). "Increased Particulate Air Pollution and the Triggering of Myocardial Infarction." Circulation 103: 2810-2815. Ritchie, Ingrid.; Martin, Stephen John. The Healthy Home Kit : Inspecting for Environmental Hazards, Working With Professionals to Avoid Risks, Cleaning Up Radon, Lead, Asbestos, and More! U.S. Environmental Protection Agency (EPA). Introduction to Indoor Air Quality. Report no. EPA/400/3–91/ 003, Washington, DC: U.S. Environmental Protection Agency, 1991. U.S. Environmental Protection Agency, Indoor Air Pollution: An Introduction for Health Professionals, No. 1994- 523-217/81322, 1994