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

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

Figure 9-19. Smoothed REMSAD<br />

simulation of ground-level sulfate<br />

concentrations at 1700 CDT on 28<br />

September 1999. Note the small<br />

cloud of elevated sulfate<br />

concentrations to the east of Big<br />

Bend.<br />

Table 9-12 showed that intersite correlations of observed sulfate, ranging between<br />

0.81 and 0.89, are considerably better than those for SO 2 . This is to be expected, as SO 4 has<br />

a relatively long residence time in the atmosphere as compared to SO 2 , and the SO 4 = plume<br />

that impacts Big Bend NP is likely to be more dispersed with weaker spatial gradients.<br />

The final variable considered here is TS, which is the concentration of sulfur that is<br />

contributed by both SO 2 and SO 4 = . According to Table 9-12, mean normalized biases for TS<br />

at Big Bend range from 40 to 91%, a consequence of the overestimation of SO 2 , and mean<br />

normalized errors are 62 to 206%. Correlation coefficients for TS are between 0.29 and 0.34,<br />

values that are slightly higher than those for SO 2 and SO 4 . The magnitudes and timing of the<br />

predicted TS concentrations appear to match the observations relatively well (although there<br />

is a significant amount of missing data in July) except for October, when the amount of<br />

sulfur predicted at Big Bend NP is significantly greater than the observed concentrations.<br />

Also, it is interesting that the timing of the mid-October TS peak is correct, contrasted with<br />

the premature occurrence of the simulated SO 4 peak, possibly indicating that estimated SO 4<br />

oxidation rates are too rapid during this period.<br />

A similar performance analysis was carried out for air quality monitors located along<br />

the northern, eastern, southern, and western peripheries of the <strong>BRAVO</strong> monitoring network.<br />

The monitoring sites considered include 1) the Wichita Mountains site, a Class I area in<br />

southern Oklahoma, 2) the Big Thicket site in eastern Texas near the Louisiana border, 3) the<br />

Laguna Atascosa site at the southern end of Texas near the Mexico border, and 4) the<br />

Guadalupe Mountains National Park site, another Class I area in western Texas. SO 2<br />

concentrations are overstated by REMSAD at all four sites, especially at Big Thicket, while<br />

the SO 4 = time series shows much better agreement between the observations and predictions.<br />

Details are provided in the CIRA/NPS report on the <strong>BRAVO</strong> <strong>Study</strong><br />

9-43

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