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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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<strong>in</strong>to a category named "UNID." The source profile data reported <strong>in</strong> units of ppbC or ppbv are<br />

converted to µg/m 3 prior to calculat<strong>in</strong>g <strong>the</strong> weight percentages us<strong>in</strong>g species-specific conversion<br />

factors. One-sigma uncerta<strong>in</strong>ties were derived from variations among multiple measurements for<br />

a particular source type or a nom<strong>in</strong>al analytical uncerta<strong>in</strong>ty of 15 percent. The assigned<br />

uncerta<strong>in</strong>ties are <strong>the</strong> larger of <strong>the</strong> two values.<br />

The source composition profiles used <strong>in</strong> <strong>the</strong> CMB analysis are shown <strong>in</strong> Table 4.4-1.<br />

They <strong>in</strong>clude gasol<strong>in</strong>e and diesel exhaust, gasol<strong>in</strong>e liquid and vapor, commercial natural gas and<br />

liquefied petroleum gas, surface coat<strong>in</strong>gs, consumer products ,and isoprene.<br />

Gasol<strong>in</strong>e Exhaust. A profile for gasol<strong>in</strong>e exhaust was derived for this study from <strong>the</strong> four<br />

samples collected along <strong>the</strong> Harbor Freeway (HF1). Each HF1 sample was corrected for<br />

surround<strong>in</strong>g background VOC concentrations by subtract<strong>in</strong>g <strong>the</strong> Dodger Stadium sample (DS1),<br />

which preceded each HF1 sample. The composition profile <strong>in</strong>cluded CO and NOx <strong>in</strong> proportion<br />

to <strong>the</strong> sum of PAMS species. The two weekday samples generally reflect vehicle operation <strong>in</strong><br />

stop-and-go traffic and <strong>the</strong> two weekend samples reflect free-flow conditions.<br />

Diesel Exhaust. A profile for diesel exhaust was derived for this study from <strong>the</strong> three<br />

samples collected at a truck stop near <strong>the</strong> <strong>in</strong>tersection of I-10 and I-15. These samples were<br />

collected between 2:00 and 5:00 a.m. on Tuesday, October 3. Each truck stop sample was<br />

corrected for background VOC concentrations by subtract<strong>in</strong>g <strong>the</strong> average of <strong>the</strong> 2:00-2:45 a.m.<br />

samples that were collected at Industry Hills (IH1) on Monday, 10/2/00 and Wednesday, October<br />

4. The background correction was adjusted <strong>in</strong> order to yield zero abundance of MTBE <strong>in</strong> <strong>the</strong><br />

background-corrected diesel profile.<br />

Gasol<strong>in</strong>e Liquid and Vapor. Gasol<strong>in</strong>e samples that were collected and analyzed for this<br />

study consist of <strong>the</strong> two grades (regular and premium) for five brands (ARCO, Union 76, Shell,<br />

Chevron, and Mobil). In addition to profiles for <strong>in</strong>dividual samples, composites were derived for<br />

each grade of gasol<strong>in</strong>e from a comb<strong>in</strong>ation of <strong>the</strong> five brands. An overall composite liquid<br />

gasol<strong>in</strong>e profile was constructed based on this relative weight<strong>in</strong>g of 68% regular and 32%<br />

premium (Kirchstetter et al., 1999).<br />

The compositions of gasol<strong>in</strong>e headspace vapors were predicted from <strong>the</strong> measured<br />

composition of liquid gasol<strong>in</strong>e us<strong>in</strong>g <strong>the</strong> method described by Kirchstetter et al. (1999). This<br />

method is based on <strong>the</strong> proportionality between <strong>the</strong> equilibrium headspace partial pressure for<br />

each compound identified <strong>in</strong> gasol<strong>in</strong>e with its mole fraction <strong>in</strong> liquid gasol<strong>in</strong>e times <strong>the</strong> vapor<br />

pressure of <strong>the</strong> pure species. The <strong>in</strong>dividual vapor pressures are determ<strong>in</strong>ed us<strong>in</strong>g <strong>the</strong> Wagner<br />

equation.<br />

Commercial Natural Gas and Liquefied Petroleum Gas. The commercial natural gas<br />

(CNG) and liquefied petroleum gas profiles are based on samples taken <strong>in</strong> <strong>the</strong> summer of 1972 at<br />

Los Angeles, CA and <strong>in</strong> <strong>the</strong> summer of 1973 at El Monte, CA (Mayrsohn et al., 1976, 1977).<br />

Contribution of aged emissions is a plausible alternative <strong>in</strong>terpretation of <strong>the</strong>se two sources. The<br />

comb<strong>in</strong>ation of <strong>the</strong> two profiles accounts for <strong>the</strong> excess ethane and propane that typically exist <strong>in</strong><br />

most urban areas.<br />

Surface Coat<strong>in</strong>gs. A large variety of formulations are used <strong>in</strong> surface coat<strong>in</strong>gs, and it is<br />

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