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Management of Commercially Generated Radioactive Waste - U.S. ...

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16 17<br />

57. (Page 3.1.62, first paragraph) The likelihood that oxygen will be 65. (Page 3.1.65, fourth paragraph) The total-quantity <strong>of</strong><br />

introduced into the repository when it is constructed and therefore be radioactivity in curies is irrelevant. The nature <strong>of</strong> the radionuclides<br />

available to the ground water should be considered in evaluating and their pathways to man are significant.<br />

canisters. The mobility <strong>of</strong> some nuclides is also increased by the<br />

presence <strong>of</strong> oxygen. The possibilities that the copper would be a 66. (Page 3.1.67, first paragraph) Are these probabilities best<br />

resource which would attract human intrusion should also be considered. estimate probabilities, upper bound probabilities, or what?<br />

58. (Page 3.1.62, fourth paragraph) The misspelling <strong>of</strong> alumina should 67 (Page 3.1.67, second paragraph) Is 22 9 Ra a misprint for 226a?<br />

be corrected.<br />

59. (Page 3.1.62, Section 3.1.3.3) This section appears to assume<br />

long-term institutional functioning. Expectation that institutions<br />

will continue over thousands <strong>of</strong> years (or even that they will maintain<br />

68. (Page 3.167, third paragraph) Since the long-term behavior <strong>of</strong> the<br />

parameters is uncertain, risk assessment should be based on upper<br />

estimate predictions as well as on "reasonable" predictions.<br />

their control over hundreds <strong>of</strong> years) is not well-founded. 69. (Page'3.1.71, seventh paragraph) Sorption <strong>of</strong> radionuclides is<br />

"-<br />

60. (Page 3.1.64, first paragraph) The first century after closure <strong>of</strong><br />

controlled by the site-specific geology. It seems unlikely that<br />

radionucllde behavior data from one site can be applied to another site.<br />

the repository would be critical for "hands on" corrective action only<br />

if the monitoring program established some deficiency in the 70. (Page 3.1.100, first paragraph) The destruction caused by a<br />

repository. Although the radioactivity <strong>of</strong> the repository has been meteorite striking one <strong>of</strong> our large metropolitan areas is irrelevant to<br />

reduced substantially after 700 years, the threat is by no means this consideration. We have no control over where a meteorite will<br />

negligible, fall; therefore, one place is as good as another, and the possiblity <strong>of</strong><br />

a meteorite strike does not become a consideration in the location <strong>of</strong><br />

61. (Page 3.1.64, second bullet) What evidence is there that cities. The probability that a meteorite will disperse materials from<br />

technical information can be maintained for a very long time? What a deep geological repository is controllable in that the probability <strong>of</strong><br />

constitutes "a very long time"? a meteorite large enough to cause disruption is a function <strong>of</strong> depth and<br />

62. (Page 3.1.64, fourth paragraph) The definition <strong>of</strong> risk as "the<br />

can be reduced as much as desired by going deep enough.<br />

ce<br />

sum product <strong>of</strong> the magnitude <strong>of</strong> losses and the probability that the 71. (Page 3.1.100, sixth paragraph) The regional population for the<br />

losses will occur" is questionable. There is a tendency for aversion<br />

<strong>of</strong> high consequence accidents, which would imply a valuation other than<br />

types <strong>of</strong> releases considered most likely in the long term in waste<br />

disposal is the population in a river basin rather than the population<br />

a strict p-c product. within an eighty kilometer radius <strong>of</strong> the plant.<br />

63. (Page 3.1.64, seventh paragraph) This whole paragraph is very 72. (Page 3.1.101, second paragraph) Why is bone an organ <strong>of</strong><br />

questionable. Hazard indices are not based on estimates <strong>of</strong> societal principal interest? According to the BEIR work, more health effects<br />

risks compared to other societal risks, in general. There is also the would be expected from a dose to red marrow than from the same dose to<br />

question <strong>of</strong> whether the hazard <strong>of</strong> the waste after several hundred years bone. It is also probable that the liver should be considered a<br />

<strong>of</strong> decay, considering nuclides and pathways, is less than the hazard <strong>of</strong> significant organ.<br />

the ores.<br />

73. (Page 3.1.105, first paragraph) The Arthur D. Little work for EPA<br />

64. (Page 3.1.64, last paragraph) Consequence analysis for any found that spent fuel heat loadings should be about the same for<br />

release is the estimation <strong>of</strong> the effect <strong>of</strong> that release. It is not granite and salt. This seems reasonable considering that the salt has<br />

restricted to postulated worst cases, a higher conductivity than the hard rocks and is surrounded by shale<br />

which is not a good conductor. We would like to correct this<br />

discrepancy between the DOE and A.D. Little heat loading models.<br />

t

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