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METO 637 Lesson 19

METO 637 Lesson 19. NO x emission inventory VOC Emissions

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Page 1: METO 637 Lesson 19. NO x emission inventory VOC Emissions

METO 637

Lesson 19

Page 2: METO 637 Lesson 19. NO x emission inventory VOC Emissions

NOx emission inventory

28%

13%

5%30%

19%

5%Fuel Combustion- Electric Utility

Fuel Combustion- Industrial

Fuel Combustion- Other

On-RoadVehicles

Non-RoadVehicles

All Other

Page 3: METO 637 Lesson 19. NO x emission inventory VOC Emissions

VOC Emissions

33%

7%

29%

13%

18% SolventUtilization

Storage &Transport

On-RoadVehicles

Non-RoadVehicles

All Other

Page 4: METO 637 Lesson 19. NO x emission inventory VOC Emissions

Sulfur Dioxide emissions

67%

17%

4%

3%2%

7%

Fuel Combustion- Electric Utility

Fuel Combustion- Industrial

Fuel Combustion- Other

MetalsProcessing

Non-RoadVehicles

All Other

Page 5: METO 637 Lesson 19. NO x emission inventory VOC Emissions
Page 6: METO 637 Lesson 19. NO x emission inventory VOC Emissions
Page 7: METO 637 Lesson 19. NO x emission inventory VOC Emissions

A Typical Day in a Pollution Episode

•A common severe pollution weather pattern occurs when high pressure is centered just west of the Mid Atlantic region.

•Circulation around the high pressure center moves pollution from points west into the mid-Atlantic.

H

Page 8: METO 637 Lesson 19. NO x emission inventory VOC Emissions

Fort Meade profile 6/19/2001

Page 9: METO 637 Lesson 19. NO x emission inventory VOC Emissions

After Sunrise Ozone Levels Increase Sharply

• The ground heats up and the warm air above it erodes the inversion.

• Ozone and other compounds above the inversion layer mix with the pollution under the layer.

• This causes a dramatic increase in ground-level ozone, beginning around 10 AM.

Temperature

Alt

itu

de

Sub. inv.

Noct. inv.

Page 10: METO 637 Lesson 19. NO x emission inventory VOC Emissions

Ozone Levels Reach a Maximum in the Afternoon

Temperature

Alt

itu

de

Sub. inv.

Temperature

Alt

itu

de

Sub. inv.

Noct. inv.

Page 11: METO 637 Lesson 19. NO x emission inventory VOC Emissions

After Sunset• If the weather remains

the same, the temperature inversion forms again after dark.

• Ozone concentrations above the inversion remain at a constant, relatively, high level.

• Ozone trapped under the inversion reacts with other pollutants, and the surface; the ozone concentration diminishes. Ozone concentration

remaining constant

Ozone concentration diminishing

Temperature Inversion

Temperature

Alt

itu

de

Page 12: METO 637 Lesson 19. NO x emission inventory VOC Emissions

Westerly transport is often present when the highest ozone is observed in the mid-Atlantic.

24 hr. Back-trajectories on days of 1-hr. ozone exceedances from 1997 through 2002, Baltimore area

Page 13: METO 637 Lesson 19. NO x emission inventory VOC Emissions

Aircraft measurements of ozone

Page 14: METO 637 Lesson 19. NO x emission inventory VOC Emissions

Aircraft measurements of Sulfur Dioxide

Page 15: METO 637 Lesson 19. NO x emission inventory VOC Emissions

Upper level windsUpper level windsfrom the west…from the west…

……are turned by theare turned by thelee side troughlee side trough

Lee Side T

rough

daytimedaytime

Page 16: METO 637 Lesson 19. NO x emission inventory VOC Emissions

Low Level Jet

nighttimenighttime

Air pollution from the southwest…Air pollution from the southwest…

……comes into Maryland overnightcomes into Maryland overnight

Page 17: METO 637 Lesson 19. NO x emission inventory VOC Emissions

Plot of low-level winds from the Fort Meade, MD wind profiler during a high ozone episode

LLJLLJ LLJ

Page 18: METO 637 Lesson 19. NO x emission inventory VOC Emissions

9:00 PM 11:00 PM 01:00 AM

03:00 AM 05:00 AM 07:00 AM

Rapid Update Cycle (RUC)

model depiction of

the LLJduring a high ozone period

(high wind speeds in red).

Page 19: METO 637 Lesson 19. NO x emission inventory VOC Emissions

All three modes of transport are important when the highest pollution values are observed in the mid-Atlantic.

•Large scale ~ 800 km (~70-100 ppbv)(Much of the Eastern US)

•Medium scale ~ 200- 800 km(Carolinas to New England Region)

•Small scale ~ 100 km(N. Virginia to Baltimore,Research Triangle to NC/VA border)

Modes of Transport

Page 20: METO 637 Lesson 19. NO x emission inventory VOC Emissions

Sources

• Different types of transport imply different types of sources– Local transport Cars, industry, and other

sources in the local area– Long distance transport Primarily power plants to

W, though plumes from cities certainly contribute.

– Low level jet Primarily cars and other

low level sources; moves from SW to NE

Page 21: METO 637 Lesson 19. NO x emission inventory VOC Emissions

Effects of the August 15, 2003 Blackout on Air Quality

Compared with Aug 4, 2002

Coming soon to GRL

Selinsgrove, PA

Page 22: METO 637 Lesson 19. NO x emission inventory VOC Emissions

Effects of the 2003 Blackout on Air Quality

CEM data indicatereductions of 60-80%

L. Marufu, B. Taubman, B. Doddridge et al.

Page 23: METO 637 Lesson 19. NO x emission inventory VOC Emissions

Effects of the 2003 Blackout on Air Quality

Page 24: METO 637 Lesson 19. NO x emission inventory VOC Emissions

In summary

• It isn’t all transport…• It isn’t all local…• It isn’t all power plants…• It isn’t all automobiles…• The problem will not be solved by addressing

any one of these problems individually. ALL of these will have to show significant reductions for us to breathe clean air.