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EIS-0113_Section_11 - Hanford Site

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1 0<br />

2,13 243<br />

1<br />

4.<br />

4.<br />

8. P. 3.10, <strong>Section</strong> 3.3: What is the basis for choosing<br />

the year 2190 for loss of active institutional<br />

controls? The assurance requirement at 191.14(a)<br />

2.5.1<br />

allows credit for nomore than 100 years of active<br />

inst IIutional controls.<br />

2.4.1.16<br />

6<br />

9. Pp. 3.19 - 3.28, <strong>Section</strong>s 3.3.2 and 3.33: Disposal of<br />

Off wastes makes those wastes subject to 40 CFR 191.<br />

In scenarios where those wastes are disposed of in-place,<br />

we are concerned that compliance with 40 FEW 191 assurance<br />

requirements d, e, and f may not be achieved. Therefore,<br />

EPA believes that further consideration and analyses are<br />

necessary to evaluate the appropriate alternative for these<br />

wastes including the finalization of a design for the protective<br />

barrier and research and analysis of its longevity and longterm<br />

effectiveness.<br />

Further, for TWO wastes disposed of previously, EPA 'encou rages<br />

further action for their stabilization. We also believe that<br />

in the course of determining an appropriate action the resulting<br />

risks of all the considered alternatives should be .compared in<br />

3.<strong>11</strong>.3.31<br />

a cost-effectiveness analysts using the requirements of 40<br />

CFR 191 as a baseline.<br />

3.4.1.5<br />

10. P. 3.34, <strong>Section</strong> 3.4.1.1: Annual doses to individuals<br />

need to be discussed in this <strong>Section</strong>.<br />

<strong>11</strong>. P. 3.43, <strong>Section</strong> 3.4.1.8: The reference to 40 CFR 191<br />

should be removed. First, there are no population<br />

4.2.55<br />

standards<br />

n04<br />

ablett 4 theE processn of decontamination and<br />

decommissioning.<br />

12. P. 3.43, <strong>Section</strong> 3.4.2, second paragraph, lines 8<br />

and 9:. DOE needs to recognize here, as is done is<br />

other places in the paragraph, the difference between<br />

active and passive institutional controls. To simply.<br />

state that institutional control would make intrusion<br />

accidents unrealistic is not acceptable. Active<br />

cantr'ols ma y be considered viable but Only for a<br />

4.2.6 limited rime (100 years m um). As stated later in<br />

the text, EPA has n assumed that passive controls<br />

will ever prevent any type of intrusion but rather that<br />

they may significantly reduce the chance Of systematic<br />

intrusion. In light of this, the statement needs to be<br />

clarified and an explanation given for why intrusion<br />

accidents Mould not be realistic.<br />

13. Pp. 3.55 - 3.58, Tables 3.14 - 3.I7: Many of the<br />

values exceed 191.15 even though only the drinking<br />

wa ter pathway paway is considered; however, there is notime 3 , 5 , 5 . Q 3<br />

given for when these doses occur in Tables 3.15 and<br />

3.16. For the purposes of 40 CFR 191, all potential<br />

pathways Dead to be identified antl aP.1,bed and the<br />

maximum annual doses occurring in the first 1,000 Years<br />

identified. This is true for both wh ol e-boar and Organ 4 , 25 .5<br />

dose estimates.<br />

14. Pp. 3.56 - 3.57, Tables 3.15 - 3.16: . The units of<br />

measurement need to be given.<br />

15. Pp. 3.59 and 3.61, Tables 3.18 and 3.19: There should<br />

be an indication as towhether the reported dose<br />

equivalents are the maximum Or some other measurement.<br />

p<br />

3 .5.5.18<br />

16. Pp. 3.59, 3.61, and 3.62, Tables 3.18 - 3.20: It is<br />

noted that the "no disposal action" alternative<br />

violates 191.15 in all three tables when averaged<br />

annually over 70 years. The same s true in Table 3.20<br />

for the "in-place' and "reference" al t, relatives.<br />

37. Pp. 3.51 and 3.64, section 3.4.2.3, final sentence:<br />

There is no substantiation for the statement that<br />

intrusion accidents following the choice of the no<br />

disposal action alternative eoulo not be realistic If<br />

DOE chose that alternative. The implication is that<br />

4 . 2 . 7<br />

4.2 . 6<br />

active institutional controls Will always be present.<br />

While that may be DOE's desire, it should not be<br />

assumed that will be possible in the future simply<br />

-<br />

because DOE chooses the alternative. Further, that<br />

reasonshould not be used to rule out the scenario.<br />

This entire subject is the reason that EPA requires<br />

that active institutional controls be given credit<br />

for no more than 100 years of effectiveness.<br />

18. P. 3.68, Table 3.26: The meaning of the footnote is 4.2 . 55<br />

uncertain and needs to be clarified.<br />

4 .2.<br />

19. P. 3.70,. Table 3.28: First, the unit "2 L/day/yr" is<br />

Confusing, "2 L/day" is sufficient Since the total-body L<br />

dose is described as annual. Second, it is noted that<br />

the dose equivalents on the bottom line for in-place<br />

stabilization and the reference alternative exceed the<br />

limits in 191.15.<br />

NECEIVED DOE-RL<br />

F-D ) 1818880<br />

WM DIVISION<br />

RECEIVED DOE-RL<br />

`."° 181986<br />

6,10<br />

WM DIVISION

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