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

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

Comparing SO 2 emissions from all sources other than the Carbón power plants, the <strong>BRAVO</strong><br />

estimate (225,000 tons/year) disagreed with the estimate of the Mexican Ministry of Energy<br />

(398,000 tons/year), a ratio of about 1.8.<br />

Incorrect boundary conditions for CMAQ could result from the overestimation of SO 2<br />

and sulfate by REMSAD along the boundaries of the CMAQ domain, as identified in<br />

Section 9.9. Specifically, compared to measurements, REMSAD overestimated sulfate<br />

concentrations along the CMAQ domain boundary by approximately 40% and SO 2<br />

concentrations there by a factor of about 3.8.<br />

For one model configuration that explored the combined effects of these factors,<br />

emissions of SO 2 and sulfate within the Mexican portion of the CMAQ domain (except<br />

emissions from the Carbón power plants) were increased by a factor of two and the<br />

REMSAD-based lateral boundary conditions for SO 2 and sulfate were scaled with CASTNet<br />

and IMPROVE observations. When these adjustments were made, model performance for<br />

SO 2 and sulfate improved over that of the preliminary base case simulation, with bias and<br />

error reduced for both species throughout the <strong>BRAVO</strong> network, as shown in Table 9-17. In<br />

the end, this simulation was selected as the CMAQ-MADRID base case simulation and<br />

served as a basis for estimating the source attributions that will be presented in Chapter 11. 1<br />

Consequently, the rest of the discussion below will address the performance of this<br />

configuration of CMAQ-MADRID.<br />

Table 9-17. Network-average CMAQ-MADRID SO 2 and fine SO 4 2– performance statistics for<br />

preliminary and final base case simulations.<br />

Statistic Weekly SO2 24-hour fine SO4 2–<br />

Units<br />

Prelim.<br />

Base<br />

Case<br />

<strong>Final</strong> Base<br />

Case<br />

Prelim.<br />

Base<br />

Case<br />

<strong>Final</strong> Base<br />

Case<br />

Observed mean µg/m 3 1.48 1.48 3.1 3.1<br />

Simulated mean µg/m 3 1.74 1.61 4.67 3.97<br />

Coefficient of<br />

Determination (r 2 )<br />

0.45 0.46 0.47 0.47<br />

Mean bias µg/m 3 0.26 0.12 1.57 0.87<br />

Mean error µg/m 3 0.69 0.60 2.24 1.67<br />

Mean Normalized Bias % 48 40 57 37<br />

Mean Normalized Error % 71 64 82 65<br />

Fractional Bias % 15 20 18 8<br />

Fractional Error % 44 43 54 47<br />

RMS error µg/m 3 1.09 0.97 3.58 2.65<br />

1 The CMAQ-MADRID base case simulation covers the time period July 2 – October 28, which is<br />

slightly shorter than the period of the REMSAD simulation. This causes slight variations in statistical<br />

data based on observations, e.g. mean observed concentrations, compared to the corresponding values<br />

in the tables shown in Section 9.9 in conjunction with the evaluation of REMSAD performance.<br />

9-52

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