View Document Here - Hanford Site
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1• Satisfy the preference for treatment as a principal<br />
2 element.<br />
3<br />
4<br />
5<br />
19<br />
10<br />
ll<br />
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11<br />
1<br />
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2s<br />
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All of the alternatives other than Alternative 0 meet the<br />
threshold criteria for protection of human health and<br />
the environment and compliance with ARARs. thus<br />
satisfying the statutory requirements of ¢$C(.A<br />
eriteria ( 1) and (2) (see inset table on n. XX__for<br />
criteria. Alternative 6 is also the least costly<br />
alternative, is similarly or more effective than the other<br />
alternatives for the long term and short tenn, and Is<br />
considered implementable, thus satisfying the statutory<br />
requirement to be cost effective ( 3). Alternative 6<br />
provides a similar degree of permanence compared to<br />
the other alternatives because all alternatives involve<br />
hazardous substance disposal on the <strong>Hanford</strong> <strong>Site</strong>. The<br />
use of grout to fill void spaces will act as a treatment<br />
to immobiline contaminants in the building's structure<br />
although not to the degree of<br />
Alternatives 3 and 4. Orouting will serve to help<br />
satisfy the statutory requirements in (4) and (5),<br />
although none of the alternatives Include treatment as a<br />
principal element.<br />
Changes to the preferred altemative presented in this<br />
Proposed Plan or changes to another alternative may<br />
be made if public comments andlor additional data<br />
Indicate that such a change would result In a tnore<br />
appropriate ckanup solution. The final decision<br />
regarding the selected interitmremedies for the 221-U<br />
Facility will be documented in a ROD after review and<br />
consideration of all comments on this Proposed Plan.<br />
DOE/RG2001-29<br />
Draft D Redline/StrikeoutB<br />
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$9<br />
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NATIONAL ENVIRONMENTAL POLICY ACT 90<br />
91<br />
Several of the evaluation criteria specified by 92<br />
CERCLA Involve consideration of environmenul 93<br />
resources, but the emphasis is often directed at 94<br />
potential adverse effects of contaminants on living 95<br />
organisms. The National Enrironmenaof PoGcy Act 96<br />
of 1969 (NEPA) process is Intended to help federal 97<br />
agencies make decisions based on an understanding of 98<br />
environmental consequences and to take appropriate 99<br />
actions that protect, restore, and enhance the 1oo<br />
environment. DOE 0 451.113 requires incorporation 101<br />
19<br />
of NEPA values into CERCLA documents, such as the<br />
221-U Final Feasibility Study and this Proposed Plan,<br />
to the extent practicable in lieu of separate<br />
documentation.<br />
The NEPA-related resources and values that have been<br />
considered for the 221-U Facility support the<br />
CERCLA docision-making process and are<br />
summarized in the following text. The No Action<br />
alternative has no impact on NEPA values and is not<br />
included in the discussion.<br />
Transportation Impacts. None of the proposed<br />
remedial alternatives would be expected to create any<br />
long-term transportation impacts. If adverse impacts<br />
to transportation were to be detected. remedial<br />
activities would be modified or halted until the impact<br />
is mitigated.<br />
Air Qtsality. Potential a'tr quality impaeu are<br />
associated with all of the alternatives. These impacts<br />
have not been quantified but in the near term would be<br />
expected to be minor. For Alternatives 1, 3. 4, and 6,<br />
impacts would be mitigated through appropriate<br />
engineering controls.<br />
Natural, Cultural, and Historical Resources. Some<br />
short-tcrm adverse impacts to natural or cultural<br />
resources could occur during Implememation of<br />
Alternatives 1, 3, 4, and 6. The area immediately<br />
around the 221-U Facility is heavily developed with<br />
little wildlife or useable habitat, so few Impacts to<br />
biological or cultural resources are anticipated at the<br />
facility.<br />
Potential impacts to these resources would be a greater<br />
concern at borrow sites because they are located in<br />
otherwise undisturbed areas. Hotrow material would<br />
be obtained on or near the Central Plateau, an area<br />
that contains important iHg--largg_sagebrush<br />
communities. In any alternative, it would be critical to<br />
avoid disturbing sagebrush communities and any other<br />
high-quality habitat. Alternative 1 would require the<br />
least amount of borrow material and therefore would<br />
have the fewest potential impacts at borrow sites.<br />
Alternatives 3 and 4 would require 17 times more<br />
borrow material than Alternative 1 and would have the<br />
greatest potential Impacts at borrow sites.<br />
Allernative6 would require about five times more<br />
borrow material than Alternative 1. In Alternative 1,<br />
there is also the potential for adverse impaets at the<br />
ERDF. which Is located in an area of high-quality<br />
shrub-steppe habitat. Alternative I would require<br />
about a 12% expansion of an ERDF cell for waste<br />
disposal.