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Chapter 7 Chemistry of urban and indoor atmospheres

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Title: Chapter 7 Chemistry of urban and indoor atmospheres


1
Chapter 7Chemistry of urban and indoor
atmospheres
  • CH350/EV350
  • Spring 2008

2
WHO air quality guidelines
  • Exposure concentration x time
  • Concentration allowed over 8 hours will be less
    than that allowed for just 1 hour
  • CO limit 10 mg/m3 for 8 hours
  • CO limit 20 mg/m3 for 1 hour

3
WHO air quality guidelines
4
Air Quality in megacities (gt10 million)
  • Sulfur dioxide (SO2)
  • Bejing, Seoul, and Mexico City have ambient
    levels of SO2 that greatly exceed WHO guidelines
  • Many cities restrict coal burning and dont have
    a problem with SO2

5
Air Quality in megacities (gt10 million)
  • Suspended particulate matter (SPM)
  • 150-230 mg/m3 WHO guidelines
  • 200-600 mg/m3 average
  • Some exceed 1000 mg/m3 at times
  • Beijing, Shanghai, and Seoul particles due to
    domestic heating
  • Beijing, Cairo, Delhi, Karachi and Mexico City
    have high natural loadings of wind-blown
    particles
  • London, New York, and Tokyo consistently met
    particle guidelines

6
Air Quality in megacities (gt10 million)
  • Carbon monoxide (CO)
  • 10 mg/m3 WHO guidelines
  • Concentrations vary significantly across the city
  • Large amounts of automobiles generally contribute
    to higher amounts of CO, Mexico City, London, and
    New York

7
Air Quality in megacities (gt10 million)
  • Nitrogen dioxide (NO2) and ozone (O3)
  • Not measured as much as other pollutants
  • Mexico City, Los Angeles, and Sao Paulo, have
    short-term concentrations of NO2 and O3 that
    exceed WHO guidelines
  • Mexico City had O3 at 900 mg/m3, four times the
    guideline of 200 mg/m3

8
Air Quality in megacities (gt10 million)
  • Lead (Pb)
  • Dependent on number of cars and amount of lead in
    fuels
  • Cairo and Karachi have excessive lead levels
  • Many countries have removed lead from fuels or
    have plans to do so soon.
  • Residuals of lead in soils near roads or fueling
    areas can be a problem

9
Which city would be the worst to live in based on
atmospheric pollution?
10
Mexico City
  • Surrounded by mountains
  • Little wind
  • Often have temperature inversions
  • Pollutants accumulate and often exceed WHO
    guidelines

11
Mexico City SO2
  • SO2 always above WHO guidelines
  • Power plants burn high sulfur (3.5 S) fuel oil
  • Buses and trucks burn diesel fuel with 1.2 S
  • Power plants switching to natural gas (less
    sulfur)

12
Mexico City suspended particles
  • Particle concentrations always above WHO
    guidelines
  • Large amount of natural particles (soil dust and
    biological particles)
  • Domestic, industrial, and transportation
    combustions also significant sources of particles.

13
Mexico City CO
  • CO often a problem from morning rush hour
  • High altitude of city (lower pressure) makes it
    more likely to have incomplete combustion
  • Low pressure also contributes to adverse health
    effects related to CO.

14
Mexico City NOx and O3
  • NOx mainly from transportation.
  • NOx not too much higher than WHO guidelines.
  • Inversions often cause ozone problems 30 of days
    have ozone levels higher than national standards
  • The southwest sector of city has 60 of days
    where ozone levels exceed standards.

15
Mexico City Pb
  • Amount of lead in atmosphere peaked in 1980
  • Caused by lowering amount of lead allowed in
    fuels.

16
Air Quality Index (AQI) in US
  • CO, NO2, PM2.5, SO2, O3, and Pb measured to
    determine air quality.

17
AQI criteria
18
AQI Health Effects
19
2007 AQI Data CA and MO (selected areas)
20
2007 PM2.5 data for selected MO and CA cities
21
AQI for US areas
  • Any areas of interest?
  • http//www.epa.gov/air/data/geosel.html

22
Indoor air quality
  • People spend a lot of time indoors
  • Cooking, cleaning, heating by open or contained
    fires, smoking can cause changes in air quality

23
Factors affecting indoor air quality
  • Air outside
  • If air outside is polluted (O3 as an example),
    some of that air will eventually get inside.
  • Air exchange rate
  • Some airy houses have many air exchanges per hour
  • Pollutants generated inside are removed
  • Very tightly insulated houses have only 0.1 0.5
    air exchanges per hour
  • Pollutants generated inside tend to accumulate

24
Air exchangers that conserve energy
25
Air exchangers that conserve energy
26
Factors affecting indoor air quality
  • Construction materials
  • Many plastics are sources of formaldehyde
  • Clays are sources of radon
  • Indoor activities
  • Combustion for heating or cooking releases gases
    and/or particles
  • Cooking foods releases gases and/or particles
  • Smoking releases gases and/or particles
  • Cleaning creates dust and releases volatile
    solvents

27
Sources of pollutants to indoor air
28
Common indoor air contaminantsRadioactivity
  • Uranium-238 (t1/2 4.5 x 109 years) and Thorium
    -232 (t1/2 14 x 109 years) common in rocks and
    soils
  • Lead to the production of radon through alpha
    decay

29
Common indoor air contaminantsRadioactivity
  • Radon is a noble gas (t1/2 3.8 days for
    radon-222)
  • Migrates through cracks into buildings
  • Inhaled into lungs

30
Common indoor air contaminantsRadioactivity
  • Radon decays to polonium and ultimately to
    lead-206 (which is stable)
  • Polonium is not a gas and will remain in lungs if
    formed there
  • Ultimately Rn decay in lungs will lead to 3-a
    particles, 4-b particles, and Pb remaining

31
Common indoor air contaminantsVolatile organic
compounds
  • VOCs come from construction materials, consumer
    products, and combustion processes
  • Construction materials leading to VOC releases in
    New buildings is high
  • Wood composites (chips and sawdust)
  • Insulating foams
  • Floor tiles
  • Carpet
  • Adhesives used in insulation
  • Construction material VOCs include
  • Chloroform
  • Acetone
  • Chlorinated compounds
  • Formaldehyde

32
Formaldehyde release from construction materials
decreases with time
33
Formaldehyde from construction materials
  • Sources of formaldehyde include resins for
    plywood and particle board, fire-retardant
    chemicals, color retention chemicals, some
    wallpapers, and urea formaldehyde (UF) polymers
  • Release of formaldehyde is enhanced by
    temperature and humidity

34
Formaldehyde and FEMA trailers used for Hurricane
Katrina victims
  • FEMA used new mobile home trailers to help
    victims displaced by Hurricane Katrina
  • Some of these trailers had high levels of
    formaldehyde emissions
  • http//www.sierraclub.org/gulfcoast/downloads/form
    aldehyde_test.pdf
  • http//www.fema.gov/media/archives/2007/051807.sht
    m
  • http//www.homelandstupidity.us/2006/08/08/formald
    ehyde-in-fema-travel-trailers-making-people-sick/
  • Question What did these people expect to get
    from the government, old worn out homes to live
    in or new temporary homes? It shouldnt be
    surprising that new homes in a hot humid climate
    have large VOC emissions!
  • Does it not occur to people that air exchange
    rates are important and if people suspect they
    are getting sick from the air, they should open
    windows to get the bad air out!

35
VOCs from Combustion
  • Fuel to air ratio is important for VOC production
  • CO common but hydrocarbons are also produced
  • Ventilation of exhaust is important
  • In many poor countries people use wood/coal fires
    to cook in house with no chimney
  • Cigarette smoking releases aldehydes, ketones,
    organic bases, organic acids, and hydrocarbons

36
Common indoor air contaminantsIndoor particles
  • Particles can come from combustion of fossil fuel
    or biomass
  • Wood stoves, smoking, other heating/cooking
    sources
  • 100 mg/m3 acceptable standard
  • 4 methods of cooking tortillas studied in rural
    Mexico
  • 1140 mg/m3 for biomass fuel in unvented house
  • 330 mg/m3 for liquefied petroleum gas in unvented
    house
  • 540 mg/m3 for unvented biomass and liquefied
    petroleum gas
  • 430 mg/m3 for vented biomass

37
Particles produced during cooking
  • Environ. Sci. Technol., 38 (8), 2304 -2311, 2004.
  • Source Strengths of Ultrafine and Fine Particles
    Due to Cooking with a Gas Stove
  • Lance A. Wallace, Steven J. Emmerich, and
    Cynthia Howard-Reed
  • Selected parts of Abstract
  • Cooking, particularly frying, is an important
    source of particles indoors.
  • The selected cooking episodes (mostly frying)
    were capable of producing about 1014 particles
    over the length of the cooking period (about 15
    min), more than 90 of them in the ultrafine
    (lt0.1 m) range
  • Frying produced peak numbers of particles at
    about 0.06 mm.
  • Levels of PM2.5 were increased during cooking by
    a factor of 3.
  • Breakfast cooking (mainly heating water for
    coffee and using an electric toaster) produced
    concentrations about half those produced from
    more complex dinnertime cooking.

38
Particles produced during cooking
  • Environ. Sci. Technol., 41 (1), 99 -105, 2007
  • Compositions of Fine Particulate Organic Matter
    Emitted from Chinese Cooking
  • Yunliang Zhao, Min Hu, Sjaak Slanina, and
    Yuanhang Zhang
  • Selected parts from Abstract
  • In this study, the chemical composition of
    particulate organic matter (POM) in PM2.5 emitted
    from four different Chinese cooking styles were
    examined by gas chromotography-mass spectrometry
    (GC-MS).
  • The dominant homologue is fatty acids,
    constituting 7385 of the quantified compounds.
  • The pattern of n-alkanes and the presence of
    -sitosterol and levoglucosan indicate that
    vegetables are consumed during Chinese cooking
    operations.
  • The candidates of organic tracers used to
    describe and distinguish emissions from Chinese
    cooking in Guangzhou are tetradecanoic acid,
    hexadecanoic acid, octadecanoic acid, oleic acid,
    levoglucosan, mannosan, galactosan, nonanal, and
    lactones.
  • During the sampling period, the relative
    contribution of Chinese cooking to the mass
    concentration of atmospheric hexadecanoic acid
    should be less than 1.3 in Guangzhou.

39
Common indoor air contaminantsIndoor particles
  • Soil dust
  • Mold
  • Lead paint
  • Asbestos

40
Collapse of World Trade Center in 2001
  • Large amount of dust/particles created during the
    burning and collapse of towers

41
Collapse of World Trade Center in 2001
  • Dust even penetrated indoor environments of
    businesses and homes.

42
Collapse of World Trade Center in 2001
  • Particles contained
  • Asbestos
  • Polycyclic aromatic hydrocarbons (PAHs)
  • polychlorinated biphenyls (PCBs)
  • polybrominated dipheyl ethers (PBDEs)
  • polybrominated dibenzo-p-dioxins (PBDDFs)
  • tetra- and pentachlorinated biphenylenes (PCBPs)
  • This has created public concern because WTC dust
    is thought to cause adverse pulmonary symptoms
    including "WTC cough" and reduced lung capacity.
    Pleil et al. 2006

43
Particles from Laser printersEST
DOI10.1021/es802193nAuthor Lidia Morawska
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