Air is a non-homogenous mixture of gases, solid particles, and liquids.
Air is characterized as an aerosol.
Nominal Composition
| Major Components | (99%) in % by wt. | |
|---|---|---|
| N2 | 75.51% by wt. | (0.7808) |
| O2 | 23.14% | (0.2095) |
| 40Ar | 1.28% | (0.0093) |
| Water Vapor | (0.0004) |
| Minor Components | |
|---|---|
| CO2 | 325 ppm (parts per million) |
| Ne | 18 |
| He | 5 |
| CH4 | 2 |
| N20 | 0.5 |
| Xe | 0.1 |
The Atmosphere is Divided into Four Major Regions
Recall atmosphere layers
| Troposphere | 0-17, Km (? 11 mi.) | > -56°C |
| Stratosphere | 17-50 | > -2°C |
| Mesosphere | 50-90 | > -85°C |
| Ionosphere (thermosphere) | 90-100 |
95% of the air by weight is contained in the Troposphere.
An equilibrium is established which accounts for the earth's surface temperature this is the Positive greenhouse effect.
It is an increase in the shift of this equilibrium that will increase
the average temperature of the earth's surface and result in a
Negative greenhouse effect.
The Sun - The Atmospheric Energy Driver
All energy driven reactions on Earth and are a result of large amounts
of energy form the Sun.
The Atmosphere has different temperatures at different heights due to
chemical reactions driven by the Sun's energy of ~1 Kw/m2/ day at surface
and ~1,340 watts/m2/ day; in the upper atmosphere perpendicular
to the Sun.
What wavelengths are involved with the conversion of energy?
The sun is our only source of energy. It transmits ~ 86 % of
this energy at 400-700 nm (0.4 to 0.7 {µm} micrometers)
The Visible Light Spectrum. [400 nm blue and 700 nm red]
~7 % is transmitted at < 400 nm or as ultraviolet (UV).
(remember O3)
~7 % is transmitted at > 700 nm or as Infrared (IR).
Outdoor Air Pollutants
Sources and Types:
1. Carbon Oxides - Carbon Monoxide (CO), Carbon Dioxide (CO2)
2. Sulfur Oxides - Sulfur Dioxides (SO2) & Sulfur Trioxide
(SO3)
{contributor to ground level Ozone, (O3)}
3. Nitrogen Oxides - Nitric Oxide (NO), Nitrogen Dioxide (NO2),
& Nitrous Oxide (N2O)
{contributor to ground level Ozone, (O3)}
4. Volatile Organic Compounds (VOCs) - Most organic compounds
Example: Methane (CH4), Methanol (CH3OH), Benzene
(C6H6), Chlorofluorocarbons (CFCs), formaldehyde
(CH2O), Propane (C3H8).
{contributor to ground level Ozone, (O3)}
5. Suspended Particulate Matter (SPM) - Solid and Liquid Particles
both suspended in air. Example: dust soot, pollen, asbestos,
ash, conglomerates, soil, salts, etc.
{contributor to ground level Ozone, (O3)}
6. Photochemical Oxidants - Ozone (O3), Peroxide (H2O2), Complex interactions with VOCs and NOx. Photochemical reactions
7. Radioactive Isotopes - Radon - 222, Iodine - 131, Strontium - 90, Plutonium - 239, Potassium - 40,
8. Heat - Waste energy from fossil fuels; most energy sources and uses produce waste energy as heat, Ex.: cars, power, plants,
9. Noise - A byproduct of energy: airplanes, cars, industry,
lawn mowers, mechanical, radios, wind, electrical power line discharge,
etc.
Outdoor Air Pollutants
Figure 22-2 (Primary Pollutants)
Primary Pollutants Anthropogenic (Directly Emitted)
CO Carbon Monoxide
CO2 Carbon Dioxide
NO
Nitrogen Monoxide
NO2 Nitrogen Dioxide
SO2 Sulfur Dioxide
VOC Volatile Organic Carbon
SPM, Suspended Particulates Matter
or PM-10
Secondary Pollutants (Transformed in
the environment)
SO3 Sulfite
HNO3 Nitric Acid
H2SO4 Sulfuric Acid
H2O2 Hydrogen Peroxide
O3 Troposphere
Methane (CH4) {a primary VOC}, Contributor to Photochemical Smog
and Greenhouse Gas Emissions from Anthropogenic Sources
| World | 270,000,000 metric tons |
|---|---|
| By World Region | |
| Asia | 130,000,000 |
| North and Central America | 45,000,000 |
| Europe | 26,000,000 |
| USSR | 34,000,000 |
| Africa | 19,000,000 |
| South America | 19,000,000 |
| Oceannia (Australia, Fiji, etc.) | 6,200,000 |
Outdoor Air Pollutants
Pollution Emissions
Anthropogenic compositional alterations to the atmosphere:
From 1989 Compilation (from United Nations Reference)
Emissions of Chlorofluorocarbons (CFCs)
| World | 580,000 metric tons |
|---|---|
| By World Region | |
| Asia | 140,000 |
| North and Central America | 150,000 |
| Europe | 180,000 |
| USSR | 67,000 |
| Africa | 16,000 |
| South America | 15,000 |
| Oceannia (Australia, Fiji, etc.) | 9,000 |
Ozone depletion is the main effect, remember on average each Cl atom destroys 100,000 (105) O3 molecules (4 per molecule of CFC).
Pollutant Trends
From 1900 to 1970 dramatic increases in the U.S. in some pollutants
were observed.
NOx 690%
VOC 260%
SO2 210%
From 1986-1995 U.S. Concentrations of key pollutants decreased by:
NOx 14%
Ozone 6%
PM-10 22% (Particulate Matter, <10 µm)
SO2 37%
lead 78%
CO 37%
From 1986-1995 U.S. Emissions of key pollutants decreased by:
NOx 3%
VOC 9%
PM-10 17% (Particulate Matter, <10 µm)
SO2 18%
lead 32%
CO 16%
While you can measure Toposhpereic Ozone it is not (in general) a direct emission but is the result of reactions catalyzed or caused by other pollutants.
Smog and Acid Deposition Conc.
Photochemical Smog is the interaction of electromagnetic radiation from
the Sun and Primary Pollutants to form photochemical smog.
Table of Atmospheric Trace Gases in Dry Air Near Ground Level
| Gas or Species | Volume Percent | Major Source | Process for Removal |
| CH4 | 1.6x10-4 | Biogenic | Photochemical |
| CO | ~1.2x10-5 | Photochemical, Anthro | Photochemical |
| N2O | 3x10-5 | Biogenic | Photochemical |
| NO & NO2 | 10-10 - 10-6 | Photochemical, Lightning, Antho | Photochemical |
| HNO3 | 10-9 - 10-7 | Photochemical | Precipitation (rain) |
| NH3 | 10-8 - 10-7 | Biogenic | Photochemical, rain |
| H2 | 5x10-5 | Biogenic, Photochem | Photochemical |
| H2O2 | 10-8 - 10-6 | Photochemical | Precipitation |
| HO | 10-13 - 10-10 | Photochemical | Photochemical |
| HO2 | 10-11 - 10-9 | Photochemical | Photochemical |
| H2CO | 10-8 - 10-7 | Photochemical | Photochemical |
| SO2 | ~2x10-8 | Anthropogenic, Photochem, volcanic | Photochemical |
| CCl2F2 | 2.8x10-5 | Anthropogenic | Photochemical |
| H3CCCl3 | ~1 x 10-8 | Anthropogenic | Photochemical |
NOx as Outdoor Air Pollutants
NO2 & N2O Emissions 1989 1980
North & Central Am. 21,600,000 22,300,000
Asia 1,400,000
?
Europe
~15,000,000 ?
USSR 4,190,000 ?
U.S. evaluation of sources
Fuel combustion 46% of emissions
Transportation 47% of emissions (specific fuel combustion)
Industrial and other sources make up the remaining 7%
Principle anthopogenic source of NOx compounds is from fuel in
high temperature combustion processes:
N2 + O2 + heat (>1,000 °C)<--->
2NO
Then NO combines with O2 in air or other oxidents to convert NO to NO2 within a few hours under normal conditions .
2NO + O2 ( or other oxidents, RO2 )---> 2NO2
All Oxides of nitrogen with water form nitric acid (HNO3 )
N2O, NO, N2O3, NO2, N2O4, N2
O5 ~ = NOx
for reference:
2NO2
+ H2O ---> HNO2
+ HNO3
Anthropogenic Prevention
Primary method of prevention is
1. reduced temperature of oxidation of fuel (or do not burn fuel) and
2. scrubbing with various bases can be used if the process permits
Note: Natural source - Lightning and Nitrogen Cycle
Good Ozone
Hypotheses of CFC effect on Ozone presented
The possible depletion of Ozone by Anthropogenic gases was first proposed by H. S. Johnson of the U. of CA, Berkeley in the 1960s.
Effect on ozone of CFCs was theorized in 1974 by two chemists, Sherwood
Rowland and Mario Molina from the University of California, Irvine.
(Noble Prize for this contribution)
Uses CFCs
Coolants in air conditioning and refrigerating
Cleaning of electrical parts
Fumigants for granaries and cargo holds
Bubbles in polystyrene plastic foam packaging & insulation
(DuPont - Styrofoam)
Propellants in aerosol spray cans (not in US since 1978s)
Demographics
MDCs (industrialized countries) use 84% of CFCs
US is 25% of global consumption of CFCs
Vehicle air conditioners account for about 3/4 of US CFC emissions
By year 2000, 75 countries will phase out all CFC use.
Why is Cl from CFCs so devastating to Stratospheric Ozone?
How long does a CFC last in the atmosphere
over 50-400 years?
Freons without any hydrogen atoms have an average life time of 100 years in the atmosphere.
Time is needed to transcend the Troposphere thermal barrier and get into the Stratosphere reach the Ozone layer and enter it.
One Cl atom can convert 10,000 to 100,000 O3
to O2 and O
Hydrogen containing CFCs only last a relatively short time and probably never make it to the Stratosphere. CH3CCl3 and CHClF2 only last 6-7 years. This is the change in CFC formulation.
What is the difference between hydrogen containing (H)CFCs and halogen saturated CFCs?
Method of destruction in Troposphere.
CHClF2
+ OH ----> H2O + CClF2
The hydroxyl radical is the natural air cleanser of the Troposphere
and can work on (H)CFCs (not CFCs).
Mechanism of Ozone decomposition
CFC travels just above the O3 layer in the Stratosphere
Ultraviolet
- UV
CF2Cl2
----> CF2Cl
+ Cl
Eq-1
It then drifts back into the lower Stratosphere where O3 is in high
concentrations
Cl + O3 ----> ClO + O2 Eq-2
Direct destruction of Ozone
ClO + O ----> Cl + O2 Eq-3
Short circuit of Step a and c of Ozone UV protection cycle.
Life of Cl atom in atmosphere is 1-2 years.
In 1-2 years, one Cl atom will repeat Eq-2
100,000 times.
One Cl atom destroys ~ 105 the # of O3 atoms.
(A very efficient reaction mechanism)
Why does Ozone absorb UV energy?
Ozone is a Resonance Structure
This resonance gives it the unique UV energy absorbing property
Photochemical Formation of Ozone in the Stratosphere and
its interaction with UV light
Photodissociation Reaction
Step a
Ultraviolet
O2(g) ----> 2O(g)
Free Radical
120 Kcal/Mol
Step b 240 - 300 nm
Ultraviolet
O(g) + O2(g) + M(g) ----> O3(g)
+ M(g)
where M(g) is another molecule such as O2 or N2 or particle to carry
away thermal energy
(Unchanged chemically)
How Ozone absorbs ultraviolet light
Step c < 308 nm
Ultraviolet
O3(g) ----> O2(g) + O(g)* +
636, 630, 558 nm
26 Kcal/mol (yellow to red light)
Back to Step b again to be regenerated if no pollutants are present
Photochemical Formation of Ozone in the Troposphere
and
its interaction with UV light VOC and NOx
Primarily a Summer time phenomena in U.S. due to heat needed in the reactions.
Tropical climates have the potential in all seasons.
NOx + VOC + Heat + Sunlight ----> Ozone
Specific important reactions
Step a: NO2 decomposes to produce oxygen atoms
NO2 + Sunlight (<430 nm) ---->O + NO
(NO2 must be regenerated)
Step b: oxygen atom combines with oxygen molecule to form ozone with
heat carried away
O + O2 (+N2, O2, M) ----> O3 (+N2,
O2, M)
Other Ozone building step and intermediates:
O3 + light (<320 nm) ----> O*(O* Excited) + O2
O* + H2O ----> 2 OH (hydroxy radical)
OHï + RH (VOC) (+ O2) ----> H2O + RO2
RO2 + NO ----> RO + NO2 (Back to Step a:)
Thus NO2 is the main ingredient however, NO2 must be regenerated
by something other than Ozone itself as in to increase the Ozone
level and this is the VOC through the OH radical.
NO + O3 ----> NO2 + O2
Thus formation of hydroxy radicals generates oxidized VOCs that regenerate NO2 and prevent NO destruction of Ozone establish a high Ozone concentration. So Ozone concentration depends on NO2, H2O, VOC, Heat and Sunlight to reach a high Tropospheric level.
Why is Tropospheric chemistry radically different
Natural Troposphere atmospheric cleansers.
The single most important intermediate reactant in photochemical processes
sunlight
H2O(g) ----> H(g) + OH(g)
or
O* + H2O ----> 2 OH (hydroxy radical)
Carbon monoxide is converted to carbon dioxide
CO(g) + HO(g) ----> CO2(g)
+ H(g)
VOCs are removed by hydroxyl radical
CH4(g) + HO(g) ----> H3C(g) +
H2O
Summary
Increases in NOx and VOC concentration on hot (due to Sunlight) days when water vapor is highest and increases the O3 level due to a complex series of reactions.
These conditions occur
Since NOx and VOC can be transported they can contribute to O3 concentrations
in other locations where water and Sunlight find them on a warm Summer
day.
What can we reduce or eliminate to reduce Ozone?
Sunlight No
Water vapor No
Heat No
Inversions  No
VOCs Some
NOx Some
Air Movement No
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