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100<br />

I Noise, Visual, and Aesthetic Effects. Alternatives 1,<br />

2 3.4. and 6 would increase noise levels, but the impacts<br />

3 would be or shurt-term duration during remedial<br />

4 actions and would not affect offsite noise kvels.<br />

5 Alternative 1 would have a positive impact on visual<br />

6 and aesthetic effects. Conversely. Alternatives 3 and 4<br />

7 and, to a lesser extent. Alternative 6 would have a<br />

8 negative long-term visual and aesthetic impact due to<br />

9 the visibility of the disposal facility from a distance.<br />

10 Under Alternatives 3 and 4, the facility would be<br />

11 approximately 24 m(80 ft) in height, and under<br />

12 Alternative 6, would be approximately 12 m (39 ft) in<br />

13 height.<br />

14 Socioeconosnie Impacts The 221-U Facility itself is<br />

15 not a factor In the socioecotwmics of the region. The<br />

16 number of workers involved in remedial actions under<br />

17 any of the alternatives would be small; therefore.<br />

18 impacts would be negligible.<br />

19 1Envlromanental Justice. Offsite impacts to any of the<br />

20 local communities would be minimal for all of the<br />

21 alternatives, so environmental justice iuues (i.e.. high<br />

22 and disproportionate adverse health and<br />

23 socioeconomie impacts on minority or low-income<br />

24 populations) would not be a concern.<br />

25<br />

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Irrevessibk and Irretrievabk Commitrnent or<br />

Resources. Depending on the alternative selected.<br />

remedial action at the 221-U Facility could require an<br />

irreversible or Irretrievable commitment or resoiuces.<br />

particularly land use and geologic materials.<br />

All of the alternatives would result in land-tue loss to<br />

some extent. Alternatives 3, 4, and 6 would have<br />

the greatest impact because they would leave all or<br />

part of the 221-U Facility in place. This would make<br />

the site unlikely to be usable for other purposes.<br />

including industrial uses, for the foreseeable future.<br />

Alternative I would also limit site use, but to a lesser<br />

extent because contamination could remain below<br />

industrial cleanup standards but above unrestricted use<br />

standards to a depth or at least 4.6 m(IS A).<br />

Contamination above industrial cleanup standards<br />

might remain at greater depths. Alternative I would<br />

also result in IaM-use loss for ERDF disposal, because<br />

the ERDF would need to be expanded by about 12% of<br />

one cell to accommodate 221-U Facility waste.<br />

45 Alternatives 1. 3. 4, and 6 also would require an<br />

46 irretrievable and irreversible commitment of resources<br />

47 in the form of geologic materials. The quantity<br />

DOFIRL-2001-29<br />

Draft D Redline/Strikeout B<br />

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required would be significantly less for Alternative 1.<br />

This material would be obtained from onsite borrow<br />

pits. In addition, there would be a small increase in the<br />

amount of material required for the closure<br />

environmental cap at ERDF. Alternatives l, 3, 4, and<br />

6 also would require an irretrievable and irreversible<br />

commitment of resources in the form of petroleum<br />

products (e.g., diesel fuel and gasoline).<br />

Cumulative Effects. The proposed remedial action<br />

alternatives could have impacts when considered<br />

together with impacts from past and foreseeable future<br />

actions at and near the <strong>Hanford</strong> <strong>Site</strong>. Authorized<br />

current and future activities in the 200 Arws that<br />

might be ongoing during remedial action Include soil<br />

and groundwater remediation; operation and closure of<br />

underground waste tanks; construction and operation<br />

of tank waste vitrification facilities; storage of spent<br />

nuclear fuel; and surveillance, maintenance, and D&D<br />

of reprocessing facilities. Other activities on the<br />

<strong>Hanford</strong> <strong>Site</strong> Include D&D of a variety of facilities,<br />

soil and groundwater remediation, removal of spent<br />

nuclear fuel from the K Basins, and operation of the<br />

Energy Northwest commercial reactor. Activities near<br />

the <strong>Hanford</strong> <strong>Site</strong> include a privately owned radioactive<br />

and mixed waste treatment facility, a commercial fuel<br />

manufaaurer, and a titanium reprocessing plant<br />

There is some potential for impacts to natural<br />

resources at onsite borrow sites, although impacts can<br />

be minimized by appropriate planning. A DOE NEPA<br />

environmental assessment aurrenilyiuteviewthat<br />

evaluated Impacts to borrow sites from ether-<strong>Hanford</strong><br />

<strong>Site</strong> projects including remediation did dees not<br />

identify significant Impacts associated with continued<br />

use of existing onsite borrow pits. TheretaFvaiunusef<br />

remediet' ferr^yl<br />

Under Alternatives 3. 4, and 6, the 221-U Facility<br />

would become a permanent above-grade structure In<br />

the 200 West Area. With Alternatives 3 and 4, the<br />

structure would be about 24.4 m(80 ft) high and<br />

visible from a distance. Depending on other<br />

remediation activities in the 200 Areas (particularly the<br />

disposition or other canyon facilities), she facility<br />

could either be one of several such structures or could<br />

become a singular man-made element in an otherwise<br />

seeniclandscape.

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