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Appendix A - Washington State Department of Ecology

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i. Factor 1: Cost <strong>of</strong> Compliance<br />

The cost effectiveness <strong>of</strong> controls is expressed in cost per<br />

ton <strong>of</strong> pollutant reduced ($/ton). 40 CFR Part 51, App. Y,<br />

IV.D.4.c. Cost effectiveness is calculated by first estimating<br />

the total capital and annual costs <strong>of</strong> the BART controls. The<br />

second step requires calculating the amounts <strong>of</strong> the pollutants<br />

which will be reduced by the control technology selected as<br />

BART. This second step compares the uncontrolled baseline<br />

emissions (i.e. emissions from current operations) to the<br />

proposed BART emissions limits. Id.<br />

APS submitted cost estimates for all feasible control<br />

options in January 2008 and submitted revised cost estimates for<br />

SCR on March 16, 2009 to reflect higher costs <strong>of</strong> construction<br />

services and materials. In our August 28, 2009 ANPRM, we<br />

presented APS’s cost estimates for emissions controls for NOx,<br />

which included the revised SCR costs submitted in March 2009,<br />

and cost estimates from the National Park Service (NPS). In the<br />

ANPRM, EPA revised the annual operating cost estimates submitted<br />

by APS based on the ratio <strong>of</strong> annual to capital costs from other<br />

facilities in the western United <strong>State</strong>s. NPS conducted an<br />

independent analysis strictly adhering to the EPA Control Cost<br />

Manual and calculated significantly lower cost effectiveness. In<br />

subsequent comments on the ANPRM, NPS submitted revised cost<br />

31<br />

K - 356<br />

Final December 2010

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