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Analysis - The Institute for Southern Studies

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As summarized below in comparison to the initial cost estimate, the updated conversion cost is the difference in the step-1 cost to the electric<br />

utility industry <strong>for</strong> continuation of the phase-out trend without the CCR rule, compared to the step-2 cost <strong>for</strong> mandatory phase-out with the rule.<br />

Dry conversion cost: Initial cost estimate Updated cost estimate<br />

Average annualized cost $1.676 billion/year $0.876 billion/year (48% reduction)<br />

Present value (PV) cost $23.2 billion PV $12.1 billion PV (48% reduction)<br />

<strong>The</strong> updated cost is also presented below after integrating the updated dry conversion cost back into the overall cost of the CCR proposed rule<br />

which contains two other cost categories as estimated <strong>for</strong> the Subtitle C option (i.e., $491 million/year <strong>for</strong> engineering control costs + $107<br />

million/year <strong>for</strong> ancillary regulatory costs).<br />

Rule total cost: (i.e., updated dry conversion cost + engineering control cost + ancillary cost)<br />

Initial cost estimate Updated estimate<br />

Average annualized cost $2.27 billion/year $1.47 billion/year (35% reduction)<br />

Present value (PV) cost $31.4 billion PV $20.3 billion PV (35% reduction)<br />

As shown above, the composite effect of the two cost update factors is they reduce the initial dry conversion cost estimate by 48%, and reduce<br />

by 35% the overall compliance cost estimate (i.e., dry conversion cost plus engineering control costs plus ancillary costs).<br />

o Factors Which May Accelerate the CCR Impoundment Phase-Out Trend<br />

For the reasons described above, it is clear that there is a significant past and continuing trend toward CCR impoundment phase-out at electric<br />

utility plants, regardless of the CCR rule, and that this trend will continue. Described below, EPA has identified seven factors which<br />

corroborate continuation of this impoundment phase-out trend, some of which have been quantified in the cost adjustment:<br />

1. Industry conversions to dry CCR disposal: This factor corroborates the phase-out trend applied in the cost update. As discussed<br />

above, there is a documented over two-decade long trend 1996 to 2019 away from wet CCR disposal in the electric utility industry.<br />

This trend consists of two parts: (a) the 1996-2005 historical data period, plus (b) the more recent (2009) announcements of actual<br />

conversions which occurred between 2005 and 2009, and planned conversions to occur within the next 10 years (i.e., by 2019).<br />

According to one company (United Conveyor Corporation) who has been supplying dry disposal equipment and conversion services to<br />

the electric utility industry, the main historical drivers <strong>for</strong> this voluntary shift have been (1) generating dry fly ash as a saleable coproduct<br />

to other industries <strong>for</strong> beneficial uses, and (2) decreasing the volume of fly ash going to impoundments to provide greater<br />

capacity <strong>for</strong> bottom ash. Since then, concern over possible future environmental release liabilities associated with CCR impoundments,<br />

and pressure from individual state governments, has led electric utility companies to consider dry conversion. TVA is the most<br />

prominent example of this trend which publicly announced 100 in 2009 it plans to convert its wet fly ash and wet bottom ash systems to<br />

100 TVA’s 20 August 2009 news release is at http://www.tva.gov/news/releases/julsep09/ccprp_other.htm<br />

99

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