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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 />

NOx Control<br />

Technology Option<br />

Table 3-9<br />

<strong>Muskogee</strong> Units 4 & 5<br />

NOx Average Visibility Cost Impact Evaluation<br />

Total Annual<br />

Cost<br />

Modeled<br />

Visibility<br />

Impairment*<br />

29<br />

Visibility<br />

Impairment<br />

Improvement<br />

from Baseline<br />

Average<br />

Improvement<br />

Cost<br />

Effectiveness<br />

($/yr) 98 th % ∆-dv* (dv) ($/dv/yr)<br />

Baseline -- 1.06 -- --<br />

LNB/OFA $4,183,600 0.32 0.74 $5.65 MM/dv<br />

LNB/OFA + SCR $61,591,200 0.14 0.92 $66.9 MM/dv<br />

* ∆-dv values included in this table represent the modeled visibility impacts only from NOx emissions<br />

associated with each NOx retrofit control scenario. Modeled visibility impairment at the Caney Creek Class I<br />

Area was used for the cost effectiveness evaluation because modeling indicated that the largest ∆-dv<br />

improvements would occur at Caney Creek.<br />

Although SCR control systems reduce modeled visibility impacts at the four Class I Areas, the<br />

incremental cost effectiveness of SCR control (with respect to visibility improvement) is very high.<br />

Incremental cost effectiveness of SCR control is in the range of $319 million per dv improvement<br />

at the Wichita Mountains. This cost is significantly higher than costs incurred at other BART<br />

applicable sources. A review of BART determinations at other coal-fired units suggests that BART<br />

cost effectiveness values are typically in the range of less than $1.0 million to approximately $13<br />

million per dv improvement. 14 The combination of low visibility impacts with LNB/OFA controls<br />

(less than 0.32 ∆-dv at all Class I Areas) and the high cost of SCR controls contribute to the large<br />

incremental cost effectiveness of SCR at the <strong>Muskogee</strong> <strong>Station</strong>.<br />

NOx Control<br />

Technology Option<br />

Table 3-10<br />

<strong>Muskogee</strong> Units 4 & 5<br />

NOx Incremental Visibility Cost Impact Evaluation<br />

Total Annual<br />

Cost<br />

Incremental<br />

Annual Cost<br />

Modeled<br />

Visibility<br />

Impairment<br />

Incremental<br />

Visibility<br />

Impairment<br />

Improvement<br />

Incremental<br />

Improvement<br />

Cost<br />

Effectiveness<br />

($/yr) ($/yr) 98 th % ∆-dv* (dv) ($/dv/yr)<br />

Baseline -- -- 1.06 -- --<br />

LNB/OFA $4,183,600 -- 0.32 -- --<br />

LNB/OFA + SCR $61,591,200 $57,407,600 0.14 0.18 $319 MM/dv<br />

* ∆-dv values included in this table represent the modeled visibility impacts only from NOx emissions associated with<br />

each NOx retrofit control scenario. Modeled visibility impairment at the Caney Creek Class I Area was used for the cost<br />

effectiveness evaluation because modeling indicated that the largest ∆-dv improvements would occur at Caney Creek.<br />

14 See e.g., BART evaluations for Xcel (Sherco, MN); Great River Energy (Coal Creek, ND); Trigen Energy<br />

Co. (CO); Entergy White Bluff Power Plant (AR).

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