Through The Haze:
Clarifying the Ground Level Ozone

September 13, 1997
Duquesne University
Symposium held on this topic

A Seminar on Science in Environmental Reporting

Further reading

Where to go for information
by Diana Sasso, Director, Information Services, Gumberg Library

"Scientific Basis of

 Good and Bad Ozone"

 
What is the Atmosphere?

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)
O223.14%(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
** 325 ppm means that 325 of each 1 million particles is CO2

The Atmosphere is Divided into Four Major Regions

Recall atmosphere layers
Troposphere0-17, Km (? 11 mi.) > -56°C
Stratosphere17-50 > -2°C
Mesosphere 50-90 > -85°C
Ionosphere (thermosphere) 90-100

95% of the air by weight is contained in the Troposphere.

 Why?
                                    Positive Greenhouse Effect
 

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
World270,000,000 metric tons
By World Region
Asia130,000,000
North and Central America45,000,000
Europe26,000,000
USSR34,000,000
Africa19,000,000
South America19,000,000
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)
World580,000 metric tons
By World Region
Asia140,000
North and Central America150,000
Europe180,000
USSR67,000
Africa16,000
South America15,000
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

The Hydroxyl radical.

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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