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23 Cards in this Set

  • Front
  • Back
which pollutants covered by national ambient air quality standards?
CO, SO2, NO2, Pb, PM10, PM2.5, O3
2 categories of ntnl ambient air quality stds
primary-protect public health
secondary-protect public welfare (visibility, bdgs)
"attainment" areas have met NAAQS, "non-attainment" areas have not
Clean Air Act Amendments of 1970
-name 4 important things included in this act
-creation of NAAQS
-Congressional control (and not EPA control) of auto emissions with a required 90% reduction of HC, CO, NOx by mid-70's
-new source performance standards (NSPS) for stationary sources
-Ntnl Emission Stds for Hazardous Air Pollutants (NESHAPS)
catalytic converter: which pollutants it affect
NOx → N2
unburned HC → H2O + CO2
CO→ CO2

created because the CAA 1970 required emissions of these 3 pollutants to be reduced
indoor air pollution sources:

Carbon Dioxide (CO2)
breathing (people and animals), combustion
indoor air pollution sources:

Carbon Monoxide (CO)
combustion/vehicle emissions (stoves, fireplaces, heaters, cigarettes, in-garage cars)
indoor air pollution sources:

Nitrogen Dioxide (NO2)
infiltration, combustion (in-garage cars, kerosene and gas space heaters, wood stoves, gas stoves, cigarettes)
indoor air pollution sources:

Ozone
infiltration of outdoor air, photocopy machines, electrostatics air cleaners → higher concentration outdoors b/c need sun
indoor air pollution sources:

Formaldehyde (HCHO)
particleboard, insulation, paneling, plywood, carpets, tile → higher concentration indoors (need to ventilate to dilute)
indoor air pollution sources:

Sulfur Dioxide (SO2)
combustion of kerosene in space heaters, gas stoves, infiltration from outdoor combustion (mainly coal combustion) → higher concentration outdoors
indoor air pollution sources:

Radon
(two precursors and two products) – uranium (Ur) → radium (Ra) → radon (Rn) → lead (Pb) and polonium (Po) (see Fig. 9.1 for more details on radioactive decay process)
• Ur and Ra (Rn precursors) are bound in minerals, Rn is a gas, and Pb and Po are electrically charged and can be inhaled or attached to particles and inhaled (carcinogenic)
• Need to ventilate crawl space to reduce risk of exposure
indoor air pollution sources:

Asbestos
insulation (for pipes, boilers, etc), flooring materials, paint, wallpaper, fire-retardant materials → only a problem if stirred up, higher concentration indoors
health effects from asbestos
o Lung cancer
o Mesothelioma – cancer of the mesothelial membrane lining the lungs
o Asbestosis – slow, debilitating disease of the lungs – scarring of lung tissue
indoor vs outdoor standards
o Indoor standards are higher in general (that is, can pollute more indoors) b/c standards are designed to protect workers, who are assumed to be healthy adults (can withstand higher exposure), while outdoor standards protect ALL people (young, old, weak, sick, etc.)
indoor vs outdoor standards for CO
higher than for outdoor b/c designed for workers, also has indoor ceiling value b/c of harmful health effects past this concentration
indoor vs outdoor standards of NO2
additionally, stringent outdoor standard b/c precursor to photochemical smog, but indoor standards do not need to be based on NO2 being a smog-precursor (no sun), so indoor standards are based only on health concerns
What acid was first noticed as dangerous to health and agriculture?

What technology and regulation were implemented to remove this acid from emissions?
o HCl (Hydrochloric acid)
o Technology: scrubber
o Regulation: 1863 Alkali Act (See section 10.1 for the details)
• Remove 95% of HCl emissions from alkali factories
• Response to scrubber technology → inexpensive and efficient method of removing hydrochloric acid from alkali factory emissions
gas-phase oxidation for converting S(IV) to S(VI)
1) SO2 oxidize in gas phase to H2SO4
2) H2SO4 and water (attracted by H2SO4) condense onto aerosol particles or cloud drop to produce H2SO4-H2O aqueous solution
3) H2SO4 dissociates into 2H+ + SO42-
***oxidation in first step
aqueouc-phase oxidation for converting S(IV) to S(VI)
1) Dissolution of SO2(g) into liquid water drops to produce SO2(aq)
2) SO2(aq) reacts with water in the drop to form H2SO3 (sulfurous acid)
3) H2SO3 dissociates into SO32- + 2H+
4) HSO3- and SO32- oxidize to SO42- (precursor depends on pH)
**oxidation in last step
o Lakes (neutralizing agents)
• Ca(OH)2(aq) + 2H+ → Ca2+ + 2H2O(aq) slaked lime (also could use NaOH(aq))
• NH4OH(aq) + H+ → NH4+ + H2O(aq) ammonium hydroxide
o Soil (buffer)
• CaCO3(s) + 2H+ → Ca2+ + CO2(g) + H2O(aq) calcite or calcium carbonate
• Like eqn 5.7
o Areas near the coast (buffer)
• NaCl(s) + H+ → HCl(g) + Na+ natural sea spray
• Like eqn 5.5
• What is the effect of acid deposition on marble and limestone buildings?
o Gypsum (CaSO4-2H2O ) crust forms on calcite surface → over time rain removes crust and leaves pits → soot from smoke deposits into pits and darkens buildings
H2SO4(aq) → 2H+ + SO42-
CaCO3(s) + 2H+ → Ca2+ + CO2 + H2O(aq)
Ca2+ + SO42- + 2H2O(aq) → CaSO4-2H2O(s)
H2SO4(aq) + CaCO3(s) + H2O(aq) → CaSO4-2H2O(s) + CO2(g) overall process