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The Pattern and Transport of Ozone in the Missouri Region Rudolf Husar and Bret Schichtel CAPITA Washington University April 9, 1997 Prepared for a briefing of the Missouri Director of Natural Resources The content of the report is based largely on the analysis conducted by the OTAG Air Quality Analysis Workgroup, including CAPITA. The comments were adapted to emphasize the conditions relevant to the state of Missouri. Limited additional analysis was conducted to document the Missouri region in more detail.
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The Pattern and Transport of Ozone in the Missouri Region Rudolf Husar and Bret Schichtel CAPITA Washington University April 9, 1997 Prepared for a briefing.

Jan 02, 2016

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Page 1: The Pattern and Transport of Ozone in the Missouri Region Rudolf Husar and Bret Schichtel CAPITA Washington University April 9, 1997 Prepared for a briefing.

The Pattern and Transport of Ozone in the Missouri Region

Rudolf Husar and Bret SchichtelCAPITA

Washington University

April 9, 1997

Prepared for a briefing of the Missouri Director of Natural Resources

The content of the report is based largely on the analysis conducted by the OTAG Air Quality Analysis Workgroup, including CAPITA. The comments were adapted to emphasize the conditions relevant to the state of Missouri. Limited additional analysis was conducted to document the Missouri region in more detail.

Page 2: The Pattern and Transport of Ozone in the Missouri Region Rudolf Husar and Bret Schichtel CAPITA Washington University April 9, 1997 Prepared for a briefing.

Missouri Ozone Concentrations and Missouri Ozone Concentrations and Background Ozone Entering the OTAG DomainBackground Ozone Entering the OTAG Domain

Average ozone concentrations in Missouri are elevated (50-65 ppb) compared to tropospheric background (30-40 ppb) found at all four corners of the OTAG domain. However, they are lower than the Ohio River Valley and the Eastern Megalopolis concentrations.

Page 3: The Pattern and Transport of Ozone in the Missouri Region Rudolf Husar and Bret Schichtel CAPITA Washington University April 9, 1997 Prepared for a briefing.

Pattern of Ozone Precursor EmissionsPattern of Ozone Precursor Emissions

The high area source emission densities of NOx are located in the vicinity of urban-metropolitan areas such as St. Louis and Kansas City.

The high point source emission densities are located mostly in the industrial Midwestern states.

Page 4: The Pattern and Transport of Ozone in the Missouri Region Rudolf Husar and Bret Schichtel CAPITA Washington University April 9, 1997 Prepared for a briefing.

Changing Average OChanging Average O33 Concentrations Concentrations

from West to Eastfrom West to East

Ozone concentration maps with west-east and north-south cross-sections.

West-east cross-section through Kansas-Ohio-Maryland. Note the accumulation of ozone from west to east.

Page 5: The Pattern and Transport of Ozone in the Missouri Region Rudolf Husar and Bret Schichtel CAPITA Washington University April 9, 1997 Prepared for a briefing.

Areas of Violations (AOV) for 1hr-120 ppb Areas of Violations (AOV) for 1hr-120 ppb and 8-hr-80 ppb Exceedancesand 8-hr-80 ppb Exceedances

Areas of violation for 1 hr - 120 ppb standard.

Areas of violation for 8 hr - 80 ppb standard.

Page 6: The Pattern and Transport of Ozone in the Missouri Region Rudolf Husar and Bret Schichtel CAPITA Washington University April 9, 1997 Prepared for a briefing.

Average Daily Max and Exceedance Rose Average Daily Max and Exceedance Rose for Ozone in St. Louisfor Ozone in St. Louis

The highest average ozone concentrations are to the north and east of the city.

The exceedances tend to occur when the wind direction is from the city.

Page 7: The Pattern and Transport of Ozone in the Missouri Region Rudolf Husar and Bret Schichtel CAPITA Washington University April 9, 1997 Prepared for a briefing.

Average Daily Max and Exceedance Rose Average Daily Max and Exceedance Rose for Ozone in Kansas Cityfor Ozone in Kansas City

The highest average ozone concentrations are to the east of the city.

The exceedances tend to occur when the wind direction is from the city.

Page 8: The Pattern and Transport of Ozone in the Missouri Region Rudolf Husar and Bret Schichtel CAPITA Washington University April 9, 1997 Prepared for a briefing.

Origin of High Ozone ConcentrationsOrigin of High Ozone Concentrations

The highest ozone concentrations occur in major metropolitan areas, Washington- New York, Atlanta, St. Louis and a large region near Ohio River Valley.

Page 9: The Pattern and Transport of Ozone in the Missouri Region Rudolf Husar and Bret Schichtel CAPITA Washington University April 9, 1997 Prepared for a briefing.

Origin of High Ozone Concentrations, Cont.Origin of High Ozone Concentrations, Cont.

Back trajectories for receptor sites for low ozone days point to outside the OTAG region as the source of low ozone.

Back trajectories for receptor sites for high ozone days point to the central OTAG region as the source of high ozone.

Page 10: The Pattern and Transport of Ozone in the Missouri Region Rudolf Husar and Bret Schichtel CAPITA Washington University April 9, 1997 Prepared for a briefing.

Role of Horizontal and Vertical TransportRole of Horizontal and Vertical Transport

Transport wind vector during low ozone days indicate transport of clean air from outside the OTAG region.

Transport wind vector during high ozone days occurs when the winds are slow and variable, except in the Northeast where they occur during westerly winds.

Page 11: The Pattern and Transport of Ozone in the Missouri Region Rudolf Husar and Bret Schichtel CAPITA Washington University April 9, 1997 Prepared for a briefing.

St. Louis Transport Speed and DirectionsSt. Louis Transport Speed and Directions

Low ozone concentrations in St. Louis are associated with ventilating flow from the southwest.

High ozone concentrations in St. Louis are associated with slower transport from the east-southeast.

Page 12: The Pattern and Transport of Ozone in the Missouri Region Rudolf Husar and Bret Schichtel CAPITA Washington University April 9, 1997 Prepared for a briefing.

Low ozone concentrations are associated with transport from the southwest as well as from the northwest.

High ozone concentrations are associated with slower transport predominantly from the southwest.

Kansas City Transport Speed and DirectionsKansas City Transport Speed and Directions

Page 13: The Pattern and Transport of Ozone in the Missouri Region Rudolf Husar and Bret Schichtel CAPITA Washington University April 9, 1997 Prepared for a briefing.

Ozone Transport VisualizationOzone Transport Visualization

Measured ozone concentration isopleths overlaid with tracer particles tracking the atmospheric flow.

Page 14: The Pattern and Transport of Ozone in the Missouri Region Rudolf Husar and Bret Schichtel CAPITA Washington University April 9, 1997 Prepared for a briefing.

Ozone in Urban and Power Plant PlumesOzone in Urban and Power Plant Plumes

The St. Louis ozone plume measured on July 18, 1975. The excess ozone within the plume is 20-30 ppb.

Ozone production in a power plant plume on August 23, 1978. Ozone production begins after about 100 km.

Page 15: The Pattern and Transport of Ozone in the Missouri Region Rudolf Husar and Bret Schichtel CAPITA Washington University April 9, 1997 Prepared for a briefing.

Spatial Pattern of High and Low Spatial Pattern of High and Low Ozone ConcentrationsOzone Concentrations

Spatial pattern of the 10th percentile of daily max. ozone. Elevated ozone concentrations are evident only in the Industrial Midwest.

Spatial pattern of the 90th percentile of daily max. ozone. Highest ozone occurs in metropolitan regions.

St. Louis and Kansas City impact their surrounding only on high ozone days.

Page 16: The Pattern and Transport of Ozone in the Missouri Region Rudolf Husar and Bret Schichtel CAPITA Washington University April 9, 1997 Prepared for a briefing.

Evidence that Precursor Emission Evidence that Precursor Emission Changes Cause Ozone ChangesChanges Cause Ozone Changes

Map of exceedances on Fridays.

Map of exceedances on Sundays.

Any control strategy that mimics the Weekday-Weekend Emission change would be effective in reducing exceedances over 120 ppb.