CRC Report No. A-34 - Coordinating Research Council
CRC Report No. A-34 - Coordinating Research Council
CRC Report No. A-34 - Coordinating Research Council
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April 2005<br />
Comparison of Source Contributions at Diamond Bar in<br />
Experiments 12 (no chemical decay) and 11 (with chemical decay)<br />
350<br />
300<br />
Expt 11 (with chemical decay) - ppbC<br />
250<br />
200<br />
150<br />
100<br />
Gasoline - day<br />
Gasoline - night<br />
(Biogenics) x 10 - day<br />
(Biogenics) X 10 - night<br />
(CNG/aged + LPG) x 10 - day<br />
(CNG/aged + LPG) x 10 - night<br />
1:1<br />
50<br />
0<br />
0 50 100 150 200 250 300 350<br />
Expt 12 (no chemical decay) - ppbC<br />
Figure 4-8. The effects of chemical reaction on concentrations of high, medium and low<br />
reactivity source categories at a mid-basin receptor (Diamond Bar).<br />
Figure 4-9 shows the effects of chemical reaction on simulated ambient concentrations at a<br />
downwind site, Crestline. As for Diamond Bar, the most heavily depleted source category is<br />
biogenic emissions, which are almost completely removed at night. However, biogenic<br />
emissions are less depleted at Crestline than Diamond Bar during the day because there are<br />
stronger local sources of biogenic emissions at Crestline. The gasoline and CNG/aged<br />
categories are more depleted by reaction at Crestline than Diamond Bar indicating that at<br />
Crestline these emissions are being transported from far upwind which allows time for even a<br />
low reactivity category such as CNG/aged (ethane) to lose about 10% to chemical reaction. The<br />
differences in the amount of chemical processing of emissions between Diamond Bar and<br />
Crestline and day vs. night show that it will be difficult to adjust a receptor model to account for<br />
chemical reactions.<br />
H:\crca<strong>34</strong>-receptor\report\Final\sec4.doc 4-18