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TOPIC 1 ATMOSPHERIC PHOTOCHEMISTRY and AIR POLLUTION INTRODUCTION TO THE CHEMISTRY OF AIR POLLUTION 12.335/12.835 EXPERIMENTAL ATMOSPHERIC CHEMISTRY, FALL 2014 RONALD PRINN & MARIA ZAWADOWICZ SEPTEMBER 23, 2014 1
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Page 1: Atmospheric Photochemistry and Air Pollution IItopic 1 atmospheric photochemistry and air pollution introduction to the chemistry of air pollution 12.335/12.835 experimental atmospheric

TOPIC 1

ATMOSPHERIC PHOTOCHEMISTRY and

AIR POLLUTION

INTRODUCTION TO THE CHEMISTRY OF AIR

POLLUTION

12.335/12.835 EXPERIMENTAL ATMOSPHERIC CHEMISTRY, FALL 2014

RONALD PRINN & MARIA ZAWADOWICZ SEPTEMBER 23, 2014

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Page 2: Atmospheric Photochemistry and Air Pollution IItopic 1 atmospheric photochemistry and air pollution introduction to the chemistry of air pollution 12.335/12.835 experimental atmospheric

a[O3]2 + b[O3] + c = 0

OZONE CYCLE & PHOTOCHEMICAL STEADY STATE APPROXIMATION (PSSA)

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Page 3: Atmospheric Photochemistry and Air Pollution IItopic 1 atmospheric photochemistry and air pollution introduction to the chemistry of air pollution 12.335/12.835 experimental atmospheric

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Page 4: Atmospheric Photochemistry and Air Pollution IItopic 1 atmospheric photochemistry and air pollution introduction to the chemistry of air pollution 12.335/12.835 experimental atmospheric

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Page 5: Atmospheric Photochemistry and Air Pollution IItopic 1 atmospheric photochemistry and air pollution introduction to the chemistry of air pollution 12.335/12.835 experimental atmospheric

The hydroxyl free radical (OH) is the major oxidizing

chemical in the global atmosphere

It annually removes about 3.7 billion metric tons (Pg) of trace gases (CO, CH4, higher hydrocarbons, hydro-halocarbons,

NOx, SOx, etc.) from the atmosphere..

With a lifetime of only about 1 second it is possible to measure locally, but not

possible to measure directly at regional to global scales.

Use measurements of the industrial

chemical CH3CCl3, whose emissions are are known and whose major sink is OH, to

indirectly estimate large scale OH variations.

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Page 6: Atmospheric Photochemistry and Air Pollution IItopic 1 atmospheric photochemistry and air pollution introduction to the chemistry of air pollution 12.335/12.835 experimental atmospheric

HOWEVER, IN

POLLUTED AIR

THERE ARE

MULTIPLE

SOURCES OF OH

DEPENDING ON

TIME OF DAY

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Page 7: Atmospheric Photochemistry and Air Pollution IItopic 1 atmospheric photochemistry and air pollution introduction to the chemistry of air pollution 12.335/12.835 experimental atmospheric

BECAUSE OZONE PRODUCTION TAKES TIME,

TRANSPORT PLAYS AN IMPORTANT ROLE IN

DETERMINING EXPOSURE LEVELS

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Page 8: Atmospheric Photochemistry and Air Pollution IItopic 1 atmospheric photochemistry and air pollution introduction to the chemistry of air pollution 12.335/12.835 experimental atmospheric

USA TROPOSPHERIC COLUMN OZONE BY SEASON (Satellite observations in DOBSON UNITS = 2.7 x 1016 molecules/cm2)

Image courtesy of Fishman, J., A. E. Wozniak, and J. K. Creilson.From Atmospheric Chemistry and Physics 3 (2003): 893–907. 8

Page 9: Atmospheric Photochemistry and Air Pollution IItopic 1 atmospheric photochemistry and air pollution introduction to the chemistry of air pollution 12.335/12.835 experimental atmospheric

As we will discuss in a later lecture, human health is affected by exposure to ozone expressed here as a function of the AOT40 Index (AOT40 = hourly ozone exposure above 40 ppb in units of ppb.hr/mo.)

NOTE: (8000 ppb.hr/mo

divided by (31x24)hr/mo

=10.75ppb)

© Benjamin Felzer, Lehigh University. All rights reserved. This content is excluded from ourCreative Commons license. For more information, see http://ocw.mit.edu/help/faq-fair-use/.

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Page 10: Atmospheric Photochemistry and Air Pollution IItopic 1 atmospheric photochemistry and air pollution introduction to the chemistry of air pollution 12.335/12.835 experimental atmospheric

FIGURES: Aerosol optical depth,

τaer

, at 0.55 μm (color bar) as

determined by the MODIS

satellite instrument for the

January to March 2001 mean

(top panel) and for August to

October 2001 mean (bottom

panel). The top panel also

shows the location of AERONET

sites (white squares) that have

been operated (not necessary

continuously) since 1996. The

bottom panel also shows the

location of different aerosol

lidar networks (red = EARLINET,

orange = ADNET, black =

MPLNET). (Ref: IPCC AR4 WG1,

Chap. 2, Fig. 2.11, 2007)

ATMOSPHERIC

AEROSOLS

DEFINITION: ALL SUSPENDED

LIQUID, SOLID & MIXED

LIQUID-SOLID PARTICLES IN

AIR EXCEPT WATER DROPLETS

& ICE CRYSTALS

e.g. BLACK CARBON, SULFATE,

ETC.

ATATATATATMMMMMOSPHERIC

AEEEROSOLS

DEFINITIOOOOOON: ALL SUSPENDED

LIQUIDDDDDD,, SOLID & MIXED

LIQUID-SOOOOOOOLID PAPAPAAPAPARTICLES IN

AIR EXCCCEPPPPT WAAATATATATATER DROPLETS

& ICCCCCE CRYRYRYRYRYYSYSYSSYSYSTATATAATATALS

e.g. BLACKKKK CARBON, SULFAFAFAAFAFATATATATATE,

ETC.

© IPCC. All rights reserved. This content is excluded from our Creative Commonslicense. For more information, see http://ocw.mit.edu/help/faq-fair-use/.

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Page 11: Atmospheric Photochemistry and Air Pollution IItopic 1 atmospheric photochemistry and air pollution introduction to the chemistry of air pollution 12.335/12.835 experimental atmospheric

TYPICAL

URBAN

AEROSOL

NUMBER (N)

DENSITY (nn), &

SURFACE AREA

(S) & VOLUME

(V) WEIGHTED

DENSITIES (nS,

nV), AS

FUNCTIONS OF

PARTICLE

DIAMETER (Dp)

TYPICAL

URBAN

AEROSOL

COMPOSITION,

ORIGIN

(primary,

secondary,

either) &

SHAPE

Sulfates [H2SO4 (aq), NH4)2SO4 (aq, s)] Black Carbon [C) (s)] Organic Carbon [CxHyOz (l, s)] Dust [Silicates (s), Clays (s), Pollens (s)] Nitrates [HNO3 (aq), NH4NO3 ) (aq, s)] Chlorides [NaCl (aq, s)] Mixtures[(H2SO4 on BC, OC, dust] Spheres (liquids) Crystals (ice, salts, minerals) Dendriform (snow, soot)

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Page 12: Atmospheric Photochemistry and Air Pollution IItopic 1 atmospheric photochemistry and air pollution introduction to the chemistry of air pollution 12.335/12.835 experimental atmospheric

Examining the chemistry and physics of air pollution, we see

that air pollution regulations affect climate by increasing CH4

(warming), decreasing H2SO

4 aerosols (warming), decreasing O

3

(cooling) and decreasing black carbon aerosols (cooling).

Regulating NOx

decreases O3

and OH

Decreasing OH

increases CH4

Regulating CO

increases OH

and decreases O3

Decreasing O3

decreases OH

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Page 13: Atmospheric Photochemistry and Air Pollution IItopic 1 atmospheric photochemistry and air pollution introduction to the chemistry of air pollution 12.335/12.835 experimental atmospheric

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12.335 / 12.835 Experimental Atmospheric ChemistryFall 2014

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