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(BRAVO) Study: Final Report. - Desert Research Institute

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<strong>Final</strong> <strong>Report</strong> — September 2004<br />

REMSAD simulates this initial plume rise. Tracer releases at the other two locations were<br />

released directly in the ambient air and thus did not have any plume rise. An example of a<br />

REMSAD simulation of the transport and dispersion of the four tracers is illustrated in<br />

Figure 9-13.<br />

Figure 9-13. Example of the<br />

REMSAD-simulated dispersion of<br />

the four tracer plumes on 28<br />

September 1999. The colored<br />

areas in this 3-dimensional view<br />

of the REMSAD modeling<br />

domain represent concentrations<br />

above 0.1 ppq. The wind is<br />

generally toward the north, so the<br />

southern ends of the colored<br />

regions are in the vicinity of the<br />

release locations. The plumes<br />

represent the tracer released<br />

from (from left to right across the<br />

bottom) Eagle Pass, San<br />

Antonio, Houston and (the green<br />

area) northeast Texas.<br />

Because of the coarse grid scale of the model and the complex topography in the Big<br />

Bend region, both modeled estimates and measured tracer concentrations were averaged over<br />

all three measurement sites in Big Bend National Park. (San Vicente, K-Bar, and Persimmon<br />

Gap). These three-site averages of 24-hr measurements and modeled estimates are compared<br />

for each tracer in Figures 9-14 through 9-17. Results for the Eagle Pass and northeast Texas<br />

tracers are shown for the entire four month <strong>BRAVO</strong> period, while results for the San Antonio<br />

and Houston tracers are shown for those last six weeks of the <strong>BRAVO</strong> period when the<br />

tracers were released from these sites. Note that the vertical scales of these figures are not all<br />

the same. The “mixing ratio” is equivalent to the tracer concentration in ppq by volume.<br />

Performance statistics corresponding to these figures are tabulated in Table 9-11.<br />

9-35

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