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CRC Report No. A-34 - Coordinating Research Council

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April 2005<br />

Comparison of Source Contributions at Crestline in<br />

Experiments 12 (no chemical decay) and 11 (with chemical decay)<br />

120<br />

100<br />

Expt 11 (with chemical decay) - ppbC<br />

80<br />

60<br />

40<br />

Gasoline - day<br />

Gasoline - night<br />

(Biogenics) x 2 - day<br />

(Biogenics) X 2 - night<br />

(CNG/aged + LPG) x 10 - day<br />

(CNG/aged + LPG) x 10 - night<br />

1:1<br />

20<br />

0<br />

0 20 40 60 80 100 120<br />

Expt 12 (no chemical decay) - ppbC<br />

Figure ES-2. The effects of chemical reaction on concentrations of high, medium and<br />

low reactivity source categories at a downwind receptor (Crestline).<br />

The impact of spatial heterogeneity in emissions on the relationship between actual contributions<br />

and emission contributions is illustrated n Figure ES-3. The Figure compares actual<br />

contributions in air samples to emissions contributions for 15-km square areas around 8<br />

receptors. Points that are not along the 1:1 line are for receptors/source categories where the<br />

contributions in the air are significantly different from the local emissions inventory. The largest<br />

deviations are at downwind receptors (Crestline and Lake Perris) that have relatively low<br />

emissions near the receptor but are influenced by transport from high emission areas upwind.<br />

This is an example of spatial heterogeneity in emissions that was resolved by the 5-km gridded<br />

emissions inventory. In the real-world, there also could be fine-scale heterogeneity if, for<br />

example, a monitor is located close to a large source (e.g., a point source or freeway<br />

intersection).<br />

H:\crca<strong>34</strong>-receptor\report\Final\ExecSum_r.doc<br />

ES-4

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