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Analysis - The Institute for Southern Studies

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controls like surface-impoundment phase-out, or reduced because releases are caught earlier. <strong>The</strong>se benefits, and how they relate, are described<br />

in the section below.<br />

First, even in the absence of federal regulations, CCR disposal units will not leach and cause cancers in all cases estimated through the<br />

evaluation above. Even without federal regulation, there will be facilities that discover contamination and clean the contamination up be<strong>for</strong>e<br />

cancers occur, either due to state regulations or good practice. Where exposures are identified, this RIA assumed that the pathway will be cut<br />

off (e.g., through provision of alternative water sources). Even facilities that fail to prevent contamination may detect that contamination and<br />

clean it up at a later time, although after exposure has occurred. This Step of the estimation attempted to account <strong>for</strong> these practices.<br />

To estimate the different speed and cost of groundwater remediation likely under the baseline and under the three regulatory scenarios (i.e.,<br />

Subtitle C, Subtitle D and Subtitle D Prime), this RIA began by examining the differences across states in groundwater monitoring<br />

requirements pertaining to CCR disposal units, and focused on groundwater monitoring requirements because adequate monitoring is needed to<br />

determine whether a release has occurred. This RIA assumes that, where releases of concern have been identified, and particularly where<br />

people may be at risk, drinking water pathways will be cut off and alternative drinking water will be provided. <strong>The</strong>n calculated the percentage<br />

of CCR disposed by each state, and noted which of three levels of groundwater monitoring were required:<br />

1. No monitoring requirements<br />

2. Monitoring requirements <strong>for</strong> only future newly constructed CCR disposal units<br />

3. Monitoring requirements <strong>for</strong> both future new and existing CCR disposal units<br />

<strong>The</strong>n EPA tracked the percentage of total waste that was discarded by facilities in states requiring each of these three monitoring scenarios.<br />

Exhibit 5A-9 below presents these percentages <strong>for</strong> states requiring at least some monitoring (categories 2 and 3 above) and states requiring<br />

monitoring at exiting facilities (category 3 above). <strong>The</strong> first value in the table, 91%, is the percentage of CCR discarded in landfills that impose<br />

some <strong>for</strong>m of monitoring requirements, whether <strong>for</strong> new landfills only, or <strong>for</strong> both new and existing landfills. 62% is the percent of CCR<br />

discarded in landfills that impose monitoring requirements on both new and existing CCR disposal units (a subset of the 91%). 127 Percentages<br />

are also provided <strong>for</strong> CCR that are managed in surface impoundments. Appendix K9 provides these data <strong>for</strong> each individual state.<br />

127 Some states may require monitoring only <strong>for</strong> off-site units; however, in the absence of a specific breakdown, EPA made the assumption that on-site units would be<br />

monitored in all states that require monitoring.<br />

123

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