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Weekend/Weekday Ozone Observations in the South Coast Air Basin

Weekend/Weekday Ozone Observations in the South Coast Air Basin

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(HPLC/UV). PAMS carbonyl data normally <strong>in</strong>clude only formaldehyde, acetaldehyde, and<br />

acetone. Total non-methane organic compounds (NMOC) are <strong>the</strong> sum of quantifiable peaks by<br />

EPA method TO-14A, <strong>in</strong>clud<strong>in</strong>g unidentified but exclud<strong>in</strong>g halocarbons, or by cont<strong>in</strong>uous<br />

<strong>in</strong>struments with flame ionization detection. Measured NMOC will be lower for laboratories<br />

employ<strong>in</strong>g water management. NMOC also refers to <strong>the</strong> sum of NMHC plus carbonyl<br />

compounds by TO-11.<br />

3.1 <strong>Weekday</strong> Differences <strong>in</strong> Peak Levels and Diurnal Variations of <strong>Ozone</strong><br />

Historic trends <strong>in</strong> <strong>the</strong> average daily maximum hour ozone <strong>in</strong> <strong>the</strong> SoCAB show that both<br />

<strong>the</strong> magnitude and spatial extent of <strong>the</strong> weekend ozone effect have <strong>in</strong>creased over <strong>the</strong> period<br />

from 1981 to 1998, especially dur<strong>in</strong>g <strong>the</strong> 1990’s. Reductions <strong>in</strong> peak ozone levels <strong>in</strong> <strong>the</strong> central<br />

portion of <strong>the</strong> bas<strong>in</strong> were also greater dur<strong>in</strong>g <strong>the</strong> 1990s. Data for <strong>the</strong> summers of 1999 and 2000<br />

show a cont<strong>in</strong>uation of <strong>the</strong>se trends through <strong>the</strong> end of <strong>the</strong> decade. Figures 3.1-1a through 3.1-1d<br />

show <strong>the</strong> mean diurnal variations <strong>in</strong> ozone mix<strong>in</strong>g ratios on Saturdays, Sundays, and weekdays<br />

for <strong>the</strong> years 1980-85, 1986-1990, 1991-94, 1995-98, and 1999-2000 for Los Angeles – North<br />

Ma<strong>in</strong>, Azusa, Upland, and Rubidoux (listed <strong>in</strong> order of location from <strong>the</strong> western to eastern<br />

portion of <strong>the</strong> bas<strong>in</strong>), respectively.<br />

In <strong>the</strong> early 1980s, <strong>the</strong> highest ozone levels occurred on weekdays at Upland and<br />

Rubidoux, and on Saturdays and weekdays at Azusa. Occurrences of highest peak ozone levels<br />

on Sundays were observed at Los Angeles – North Ma<strong>in</strong>. By <strong>the</strong> late 1990s, <strong>the</strong> highest ozone<br />

levels occur on Sundays at all sites with <strong>the</strong> exception of Rubidoux where <strong>the</strong> highest ozone<br />

occurred on Saturday. The largest reductions <strong>in</strong> peak ozone levels over <strong>the</strong> past two decades are<br />

<strong>in</strong> <strong>the</strong> central bas<strong>in</strong>. In <strong>the</strong> western bas<strong>in</strong>, represented by Los Angeles – North Ma<strong>in</strong>, <strong>the</strong> mean<br />

peak current (1999-2000) ozone levels are about 60 ppb lower than <strong>in</strong> 1980-85 for all days of <strong>the</strong><br />

week. In contrast, decreases <strong>in</strong> peak ozone <strong>in</strong> <strong>the</strong> central bas<strong>in</strong> (Azusa and Upland) have been<br />

greater on weekdays (~ 100 to 110 ppb) than on Saturdays (~ 70 to 90 ppb) or Sundays (60 to 70<br />

ppb). While <strong>the</strong> reductions <strong>in</strong> peak ozone for weekdays were roughly l<strong>in</strong>ear over <strong>the</strong> past two<br />

decades, most of <strong>the</strong> reductions on weekends occurred dur<strong>in</strong>g mid to late 1990’s. The diurnal<br />

variations of ozone at Los Angeles – North Ma<strong>in</strong> show a shift of about 2 hours <strong>in</strong> <strong>the</strong> tim<strong>in</strong>g of<br />

peak ozone dur<strong>in</strong>g <strong>the</strong> past two decades. While ozone reached its peak earlier <strong>in</strong> <strong>the</strong> western<br />

bas<strong>in</strong> <strong>in</strong> <strong>the</strong> 1980s and early 90s, <strong>the</strong>re is now little difference <strong>in</strong> <strong>the</strong> tim<strong>in</strong>g of maximum ozone<br />

between <strong>the</strong> western and central bas<strong>in</strong>. With decreas<strong>in</strong>g rates of ozone accumulation and<br />

<strong>the</strong>refore lower ozone concentrations, we speculate that <strong>the</strong> onset of ventilation has become a<br />

more significant factor <strong>in</strong> <strong>the</strong> diurnal variation of ozone <strong>in</strong> <strong>the</strong> western bas<strong>in</strong>. Diurnal variations<br />

<strong>in</strong> patterns of transport and solar radiation, factors that have not changed with time, are probably<br />

more important <strong>in</strong> <strong>the</strong> tim<strong>in</strong>g of maximum ozone <strong>in</strong> downw<strong>in</strong>d areas.<br />

The plot of <strong>the</strong> mean day-of-<strong>the</strong>-week variations <strong>in</strong> daily maximum ozone mix<strong>in</strong>g ratios<br />

<strong>in</strong> Figure 3.1-2 shows that <strong>the</strong> weekday differences are similar throughout <strong>the</strong> western and<br />

central bas<strong>in</strong>. Table 3.1-1a lists <strong>the</strong> mean daily maximum ozone at Los Angeles – North Ma<strong>in</strong>,<br />

Azusa, Pico Rivera, and Upland by day of <strong>the</strong> week for summer 1999 and 2000. Ratios of <strong>the</strong><br />

mean daily maximum ozone to <strong>the</strong> midweek values (mean of Tuesday to Thursday) are shown <strong>in</strong><br />

Table 3.1-1b. The peak ozone levels on Sundays and Saturdays are about 40 and 25 percent<br />

higher than midweek values, respectively. The majority of ozone exceedances <strong>in</strong> <strong>the</strong> SoCAB<br />

now occur on Sundays.<br />

3-2

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