Background
During the summer months, high ground-level
ozone concentrations are observed within and downwind of many
of the large urban areas in the eastern US. Peak hourly average
concentrations exceed the current National Ambient Air Quality
Standard (NAAQS) for ozone of 0.12 ppm and peak 8-hour average
concentrations rise above the recently proposed revised ozone
NAAQS level of 0.08 ppm. Figure 1 shows nonattainment areas with
respect to the current 1-hour NAAQS; Figure 2 shows those areas
with design values in excess of the proposed 8-hour standard.
A significant feature of ozone concentrations in the East is that,
in contrast to other parts of the country, ozone concentrations
well in excess of the 30 - 40 ppb tropospheric background level
are observed throughout most of the eastern U.S., including locations
outside of the major urban nonattainment areas. As a result of
these large-scale elevated ozone events and the proximity of nonattainment
areas to one another, many states have found that NAAQS attainment
cannot be achieved with any reasonable level of local emission
control measures and therefore that a regional, multi-state emission
control strategy is necessary. The Ozone Transport Assessment
Group (OTAG) was formed to deal with this issue.
Figure 1. Areas not in attainment of the current 1-hour 0.12 ppm air quality standard for ozone.

Figure 2. Areas not in attainment of the proposed 8-hour 0.08 ppm air quality standard for ozone.

An integrated summary of AQAWG analysis results as they pertain to these six key areas is provided In the following sections. This is followed by a discussion of recommendations for future analyses. Summaries of each individual analysis are provided in the final section of this volume.
Table 1. Technical analyses conducted under the auspices of the Air Quality Analysis Workgroup.
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Spectral Decomposition of O3 time Series (Rao et al, 1996) |
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Trajectory Residence Time Analysis (Wishinski and Poirot, 1996; Poirot and Wishinski, 1996) |
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Source Regions of Influence (Schichtel and Husar, 1996; Schichtel, 1997) |
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Source Apportionment Model Results (Morris, 1997) |
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Transport impact distance analysis (Rao, 1996) |
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Ozone Pattern Analysis (Husar, 1996; Falk and Husar, 1996; Husar, 1997; Poirot, 1997) |
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Model/Measure comparisons at nine regional sites (Hartsell and Edgerton, 1996) |
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Site Selection for Model Evaluation (Poirot, 1996) |
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Observed/Predicted isoprene comparison (Edgerton, 1996) |
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Nashville/Middle TN Ozone Study (Meagher, 1996; Imhoff, 1996; TVA, 1996) |
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Tracer Relationships at SOS-SCION Sites (Edgerton and Hartsell, 1996) |
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Intra-Annual and High Frequency Variations at SOS-SCION sites (Vukovich, 1996) |
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Representativeness of 1995 Ozone Season (Chinkin et al, 1996) |
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Review of Ozone Trend Studies (Morris, 1996) |
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Tracer relationships at a site in South-Central PA (Edgerton, 1996) |
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Analysis of low-level jets using NARSTO Northeast data (Korc et al., 1997) |
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1. A "Y" in this column indicates related documentation
is available on the AQAWG world wide web page at the following
URL: http://capita.wustl.edu/OTAG/
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