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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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show that hydroxyl radical mix<strong>in</strong>g ratios <strong>in</strong>crease with decreas<strong>in</strong>g NO x mix<strong>in</strong>g ratios. Daytime<br />

nitric acid production has decreased between 1987 and 2000 due to <strong>the</strong> decrease <strong>in</strong> VOC mix<strong>in</strong>g<br />

ratios. Now <strong>the</strong> production of HNO 3 would be expected to be lower by about 9 ppb between<br />

weekend and weekday. PAN, HCHO, aldehyde and organic nitrates have been reduced due to<br />

reductions <strong>in</strong> VOC mix<strong>in</strong>g ratios but <strong>the</strong>ir mix<strong>in</strong>g ratios are not strongly affected by <strong>the</strong> NO x<br />

mix<strong>in</strong>g ratios at current concentrations so a weekend effect is not expected for <strong>the</strong>se species.<br />

Our simulations for EKMA are consistent with a study by Milford et al. (1994) as quoted<br />

by F<strong>in</strong>layson-Pitts and Pitts (1999). Milford et al. found that for conditions that are similar to<br />

present-day conditions <strong>in</strong> <strong>the</strong> SoCAB on Sundays (i.e., VOC near 300 ppbC and NO x at 20 to 30<br />

ppb) <strong>the</strong> rate of ozone production <strong>in</strong>creases with decreas<strong>in</strong>g NO x concentrations. The study<br />

showed that an ozone disbenefit results if present-day Sunday NO x concentrations are reduced.<br />

The Milford et al. (1994) study also shows that ozone production rates <strong>in</strong>crease dur<strong>in</strong>g <strong>the</strong> day<br />

because NO x is consumed faster than VOC, which <strong>in</strong>creases <strong>the</strong> VOC to NO x ratio. Given <strong>the</strong><br />

present-day concentrations of NO x , <strong>in</strong>creases <strong>in</strong> its emissions dur<strong>in</strong>g <strong>the</strong> day will decrease, not<br />

<strong>in</strong>crease, ozone production rates. However, based on <strong>the</strong> Milford, et al. study <strong>the</strong> NO x tim<strong>in</strong>g<br />

hypo<strong>the</strong>ses will become an important mechanism at <strong>the</strong> same po<strong>in</strong>t when reductions <strong>in</strong> NO x<br />

emissions lead to lower ozone production rates. Model<strong>in</strong>g studies should be made with updated<br />

emissions <strong>in</strong>ventories and models to verify <strong>the</strong> our model<strong>in</strong>g results and those of Milford, et al.<br />

(1994).<br />

1.5 Recommendations<br />

The vary<strong>in</strong>g emissions that occur between weekday and weekend periods provide a<br />

natural test of <strong>the</strong> ability of air quality simulation models to simulate accurately weekdayweekend<br />

differences <strong>in</strong> precursors and ozone. One of <strong>the</strong> most important applications of this test<br />

is that it helps to probe <strong>the</strong> relative sensitivity of ozone concentrations to VOC and NOx. The<br />

Coord<strong>in</strong>at<strong>in</strong>g Research Council has sponsored a study by ENVIRON to conduct proximate<br />

model<strong>in</strong>g of weekday/weekend ozone episodes <strong>in</strong> <strong>the</strong> SoCAB us<strong>in</strong>g <strong>in</strong>put data collected dur<strong>in</strong>g<br />

<strong>the</strong> SCOS97-NARSTO field study <strong>in</strong> order to determ<strong>in</strong>e whe<strong>the</strong>r proposed hypo<strong>the</strong>ses expla<strong>in</strong><br />

<strong>the</strong> weekend ozone effect. Similar model<strong>in</strong>g is planned by <strong>the</strong> ARB after develop<strong>in</strong>g a weekend<br />

emissions <strong>in</strong>ventory for SoCAB. These model<strong>in</strong>g results should be compared aga<strong>in</strong>st <strong>the</strong><br />

measured temporal and spatial variations of ozone and ozone precursors. These operational<br />

evaluations of model<strong>in</strong>g results should be accompanied by an evaluation of <strong>the</strong> accuracy of <strong>the</strong><br />

temporal and spatial patterns of precursor emissions on weekdays and weekends. In addition to<br />

prob<strong>in</strong>g <strong>the</strong> underly<strong>in</strong>g physical and chemical processes that drive <strong>the</strong> weekend effect, a series of<br />

model<strong>in</strong>g runs should be made us<strong>in</strong>g plausible alternative future emissions <strong>in</strong>ventories for 5, 10<br />

and 15 years <strong>in</strong>to <strong>the</strong> future. These runs should be used to assess <strong>the</strong> direction and sensitivity of<br />

projected concentrations of ozone, PAN, nitric acid, particulate nitrate, and formaldehyde to<br />

future VOC and NOx controls. These assessments will be particularly important for downw<strong>in</strong>d<br />

areas where emissions transported from <strong>the</strong> SoCAB could transition from VOC limited to NOxlimited<br />

and for assess<strong>in</strong>g strategies that might achieve <strong>the</strong> 8-hour ozone standard <strong>in</strong> downw<strong>in</strong>d<br />

areas but <strong>in</strong>crease peak ozone concentrations <strong>in</strong> <strong>the</strong> central bas<strong>in</strong>. Species such NOy, PAN,<br />

HCHO, and speciated hydrocarbons should be measured <strong>in</strong> <strong>the</strong>se downw<strong>in</strong>d area to provide<br />

corroboration of model<strong>in</strong>g results.<br />

1-20

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