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SITE INFORMATION PACKAGE FOR NATIONAL REMEDY REVIEW BOARD<br />

PART B, SECTION 9: COMPARATIVE ANALYSIS OF ALTERNATIVES<br />

communities. These include increased truck traffic, dust, noise, disruption of services<br />

and recreational opportunities, and reduced aesthetic quality.<br />

In the following sections, the comparative analysis of the remedial alternatives is presented<br />

in terms of the CERCLA threshold criteria in Sections 9.1.1 and 9.1.2, and the CERCLA<br />

primary balancing criteria in Sections 9.1.3 through 9.1.7.<br />

9.1.1 Overall Protection of Human Health and the Environment<br />

All of the alternatives, except the No Action Alternative, achieve the criterion of overall<br />

protection of human health and the environment. All of the alternatives based on<br />

Alternative 3+ rank slightly higher under this criterion than those based on Alternative 4+,<br />

regardless of which OU 2 alternative is included. The estimated implementation time frame<br />

<strong>for</strong> Alternative 4+ may be decades longer than that <strong>for</strong> Alternative 3+ and, during this time,<br />

Alternative 4+ would involve construction-related risks <strong>for</strong> workers, the community, and<br />

the environment resulting from the massive extent of long-term construction and hauling<br />

involved, which are risks that are considered to outweigh the long-term benefits of the<br />

proposed actions. Alternative 4+ would also have the greatest short-term environmental<br />

effects at offsite locations where borrow materials would be obtained. Implementation time<br />

frames are shorter <strong>for</strong> Alternative 3+, and the remedial actions are less extensive and carry<br />

fewer risks to workers, the community, and the environment.<br />

The differences in ranking under the criterion of overall protection of human health and the<br />

environment amongst the OU 2 alternatives do not outweigh the differences between<br />

Alternatives 3+ and 4+ overall. However, in balancing the overall effectiveness with shortterm<br />

risks, the ranking of the OU 2 alternatives under this criterion, from highest to lowest,<br />

is as follows: d, c, b, a, and e. The No Action Alternative ranks the lowest under this<br />

criterion because of the low level of protectiveness it would provide to human health and<br />

the environment.<br />

Remedial action effectiveness was evaluated in the FFS Report (USEPA, 2010) using both<br />

numerical groundwater models (CH2M HILL, 2007a, 2009a) and Predictive Analysis<br />

(USEPA, 2007; CH2M HILL, 2009f). In general, the groundwater models were used to<br />

estimate metals load reductions <strong>for</strong> actions involving groundwater collection, and the<br />

Predictive Analysis was used to estimate load reductions <strong>for</strong> remaining actions within the<br />

alternatives. The Predictive Analysis was initially developed to support the evaluation of<br />

alternatives in the 2001 FS Report (USEPA, 2001d), and was subsequently used to support<br />

evaluations in the Proposed Plan and ROD <strong>for</strong> OU 3 (USEPA, 2002). Documentation <strong>for</strong> the<br />

Predictive Analysis (referred to as the Probabilistic Analysis at the time) was initially<br />

provided in a 2001 Technical Memorandum titled Probabilistic Analysis of Post-Remediation<br />

Metal Loading (URS Greiner, 2001b). The Predictive Analysis was evaluated as part of the<br />

review conducted by the NAS (2005). Following the NAS review, a second technical<br />

memorandum, A Predictive Analysis <strong>for</strong> Post-Remediation Metals Loading, was prepared by<br />

USEPA (2007). This second memorandum provided clarification and additional<br />

documentation related to the Predictive Analysis, but the fundamentals of the analysis have<br />

remained unchanged since its initial development <strong>for</strong> the 2001 FS Report. To support the<br />

current ef<strong>for</strong>t, the Predictive Analysis has been updated to include data through August<br />

2009 and modified to include the remedial actions that comprise the remedial alternatives in<br />

the FFS Report (USEPA, 2010).<br />

B9-2

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