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Oklahoma Gas & Electric Muskogee Generating Station Best ...

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<strong>Oklahoma</strong> <strong>Gas</strong> & <strong>Electric</strong><br />

<strong>Muskogee</strong> <strong>Generating</strong> <strong>Station</strong> – BART Determination<br />

May 28, 2008<br />

that can result in reflective ash deposits on the waterwall surfaces. Because most heat<br />

transfer in the furnace is radiant, reflective ash can result in less heat removal from the<br />

furnace and higher exit gas temperatures. If ammonia is injected above the appropriate<br />

temperature window, it can actually lead to additional NOx formation.<br />

SNCR control systems have not been designed or installed on large subbituminous coalfired<br />

boilers, and, as described above, there are several currently unresolved technical<br />

difficulties with applying SNCR to large subbituminous coal-fired boilers (including the<br />

physical size of the boiler, inadequate NH3 mixing, and ash characteristics). Even<br />

assuming that SNCR could be installed on <strong>Muskogee</strong> Units 4 & 5, NOx control<br />

effectiveness would be marginal, and, depending on boiler exit temperatures, could actually<br />

result in additional NOx formation. Because SNCR has not been designed for, or<br />

demonstrated on, a large subbituminous coal-fired boiler, it was determined that the control<br />

technology is not applicable to <strong>Muskogee</strong> Units 4 & 5, and SNCR will not be evaluated<br />

further in the BART determination.<br />

3.2.2.2 Selective Catalytic Reduction<br />

Selective Catalytic Reduction (SCR) involves injecting ammonia into boiler flue gas in the<br />

presence of a catalyst to reduce NOx to N2 and water. Anhydrous ammonia injection<br />

systems may be used, or ammonia may be generated on-site from a urea feedstock. The<br />

overall SCR reactions are:<br />

4NH3 + 4NO + O2 → 4N2 + 6H2O<br />

8NH3 + 4NO2 + 2O2 → 6N2 + 12H2O<br />

The performance of an SCR system is influenced by several factors including flue gas<br />

temperature, SCR inlet NOx level, the catalyst surface area, volume and age of the catalyst,<br />

and the amount of ammonia slip that is acceptable.<br />

The optimal temperature range depends on the type of catalyst used, but is typically<br />

between 560 o F and 750 o F to maximize NOx reduction efficiency and minimize ammonium<br />

sulfate formation. This temperature range typically occurs between the economizer and air<br />

heater in a large utility boiler. Below this range, ammonium sulfate is formed resulting in<br />

catalyst deactivation. Above the optimum temperature, the catalyst will sinter and thus<br />

deactivate rapidly. Another factor affecting SCR performance is the condition of the<br />

catalyst material. As the catalyst degrades over time or is damaged, NOx removal<br />

decreases.<br />

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