11.07.2014 Views

Weekend/Weekday Ozone Observations in the South Coast Air Basin

Weekend/Weekday Ozone Observations in the South Coast Air Basin

Weekend/Weekday Ozone Observations in the South Coast Air Basin

SHOW MORE
SHOW LESS

You also want an ePaper? Increase the reach of your titles

YUMPU automatically turns print PDFs into web optimized ePapers that Google loves.

<strong>in</strong>terfaced to an Entech model 7100 automated preconcentrator, a Varian Saturn 2000 ion trap<br />

mass spectrometer, and a w<strong>in</strong>dows-based PC to manage <strong>the</strong> analytical and data acquisition<br />

operations. The target species <strong>in</strong>cluded C 2 to C 12 hydrocarbons, methanol, ethanol, and o<strong>the</strong>r<br />

alcohols. Also <strong>in</strong>cluded are C 2 and larger carbonyls <strong>in</strong>clud<strong>in</strong>g acetone, methyl ethyl ketone<br />

(butanone), benzaldehyde and o<strong>the</strong>rs. MTBE and o<strong>the</strong>r oxygenates used <strong>in</strong> fuels are <strong>in</strong>cluded as<br />

is isobutene, an important breakdown product of MTBE. Oxygenated compounds <strong>in</strong> surface<br />

coat<strong>in</strong>gs such as benzaldehyde, benzoic acid, and butylacetate are also <strong>in</strong>cluded, as are <strong>the</strong><br />

biogenic species isoprene, alpha and beta p<strong>in</strong>ene, and limonene. Commonly detected halocarbons<br />

are also <strong>in</strong>cluded. The detection limits for <strong>the</strong>se species are about 0.2 ppbv for all targeted<br />

species.<br />

Sta<strong>in</strong>less steel SUMMA-polished canisters of 3-L capacity were used for volatile<br />

hydrocarbon (C 2 -C 12 ) collection. These canister samples are suitable for analysis of speciated<br />

hydrocarbons by EPA Method TO-14, as well as for analyses of CO, CO 2 , methane, and<br />

oxygenated species. Prior to sampl<strong>in</strong>g, <strong>the</strong> canisters were cleaned by repeated evacuation and<br />

pressurization with humidified zero air, and certified as described below. The sampl<strong>in</strong>g<br />

procedure essentially follows <strong>the</strong> pressurized sampl<strong>in</strong>g method described by EPA Methods TO-<br />

12 and TO-14 and <strong>the</strong> EPA document "Technical Assistance Document for Sampl<strong>in</strong>g and<br />

Analysis of <strong>Ozone</strong> Precursors" (October 1991, EPA 600/8-91-215). Gas chromatography with<br />

flame ionization detector is <strong>the</strong> established technique for monitor<strong>in</strong>g volatile hydrocarbons <strong>in</strong><br />

ambient air. The DRI analytical procedure for analysis of C 2 -C 12 hydrocarbons is consistent with<br />

<strong>the</strong> EPA document "Technical Assistance Document for Sampl<strong>in</strong>g and Analysis of <strong>Ozone</strong><br />

Precursors" (October 1991, EPA 600/8-91-215). The GC/FID response is calibrated <strong>in</strong> ppbC,<br />

us<strong>in</strong>g primary calibration standards traceable to <strong>the</strong> National Institute of Standards and<br />

Technology (NIST) Standard Reference Materials (SRM) C 8 to C 20 Hydrocarbons by GC-FID<br />

Analysis of Tenax Cartridges.<br />

Heavy hydrocarbons, def<strong>in</strong>ed as hydrocarbons <strong>in</strong> <strong>the</strong> range of C 8 to C 20 , were collected<br />

us<strong>in</strong>g Tenax-TA (Alltech) solid adsorbent. The Tenax samples were analyzed by <strong>the</strong>rmal<br />

desorption-cryogenic pre-concentration, us<strong>in</strong>g <strong>the</strong> Chrompack Thermal Desorption – Cold Trap<br />

Injection unit (Chrompack International BV), followed by high resolution gas chromatography<br />

and Fourier transform <strong>in</strong>frared detection (IRD) – mass spectrometry detection (MSD) (Hewlett<br />

Packard 5890II GC, 5965 IRD and 5970 MSD)<br />

4.3 Spatial and Temporal Variations <strong>in</strong> Pollutant Concentrations and VOC/NOx Ratios<br />

This section exam<strong>in</strong>es <strong>the</strong> spatial and temporal variations <strong>in</strong> NO, NOy, black carbon, CO,<br />

MTBE, VOC and semi-volatile hydrocarbons. We recognized that meteorological conditions<br />

could be a major factor <strong>in</strong> <strong>the</strong> day-to-day variations <strong>in</strong> pollutant concentrations. Our collaborators<br />

<strong>in</strong> this study at Sonoma Technology, Inc. (STI) exam<strong>in</strong>ed <strong>the</strong> meteorological conditions on each<br />

day from September 29, 2000 to October 9, 2000. STI’s analysis showed <strong>the</strong> presence of a<br />

trough over Sou<strong>the</strong>rn California on a majority of <strong>the</strong> days dur<strong>in</strong>g <strong>the</strong> study. STI exam<strong>in</strong>ed eleven<br />

meteorological parameters and applied a subjective rat<strong>in</strong>g of favorable, not favorable, or neutral<br />

with respect to <strong>the</strong> probable <strong>in</strong>fluence of each parameter on ambient concentrations of primary<br />

pollutants. The period from Wednesday, October 4 to Saturday, October 7 was not conducive to<br />

high pollutant concentrations. The two Sundays (October 1 and 8) and both Mondays (October 2<br />

and 9) were overall neutral for pollutant buildup. Each weekend day dur<strong>in</strong>g <strong>the</strong> study was found<br />

4-5

Hooray! Your file is uploaded and ready to be published.

Saved successfully!

Ooh no, something went wrong!