ML20042C155

From kanterella
Jump to navigation Jump to search
Forwards Evaluation of Acceptable Concentration for Disposing of Wastes Containing short-lived Cm-242 in Near Surface Disposal Facilities.Evaluation Should Be Docketed Under 10CFR61 Rulemaking Activity
ML20042C155
Person / Time
Issue date: 02/25/1982
From: Johnson T
NRC OFFICE OF NUCLEAR MATERIAL SAFETY & SAFEGUARDS (NMSS)
To: Rich Smith
NRC OFFICE OF NUCLEAR MATERIAL SAFETY & SAFEGUARDS (NMSS)
References
FRN-46FR38081, RULE-PR-61, RULE-PR-WM-4 46FR38081, NUDOCS 8203300276
Download: ML20042C155 (6)


Text

V$ Q 38D dl py Q,..

I p,n-+

DISTRIBUTION FEB 0 5198 NMSS r/f PA 4* :

WM r/f gs-/j )/

WMLL r/f WMLL s/f N'N ^

TCJohnson HEMORANDUM FOR:

R. Dale Smit.h, Chief Low-Level Waste Licensing Branch REBrowning JBMartin Division of Waste Management RTLee PHl.ohaus FROM:

Timothy C. Johnson Dra -

/p[- Q. 'jx Low-l.evel Waste Licensing Branch

+

Division of Waste Management 6

'N,

SUBJECT:

CURIUH-242

a.C 4,<2.,

,d Enclosed is an evaluation to detemine an acceptable conc Tration'3 9193h'i j 9-

, np Ic '

fora r" : /s ng' o:n,iw m

6[

ti Cm-242 for disposal at near-surface disposal facilities. This should i>e docketed under our 10 CFR 61 rulemaking activity in accor%

i with our policy for preparing technical evaluations.

Original Signed By Timothy C. Johnson Low-Level Waste Licensing Branch Division of Waste Management

Enclosure:

As stated i

u L

8203300276 820225 PDR WASTE WM-4 PDR WMLL l

cmce>

c.

sunnwe >

ill 02../.2......

one>

sac ronu ais oow nacu aao OFFICIAL RECORD COPY usem asi-sz-m i

. C,

~'

EVALUATION OF Cm-242 CONCENTRATION FOR DISPOSAL

Purpose:

The purpose of this evaluation is to determine an acceptable concentration for disposing of wastes containing short-lived Curium 242 in near-surface-disposal facilities.

I

Reference:

1.

Propostd rule,10CFR61, " Licensing Requirements for Land Disposal of Radioactive Waste," Federal Register, Vol. 46, l

t No.142, July 24,1981, Table 1, p. 38097.

2.

Draft Environmental Impact Statement on 10CFR61, " Licensing Requirements for Land Disposal of Radioactive Waste,"

N'JREG-0782, Vol. 2, p. 7-16.

3.

Radiological Health Handbook, U.S. Department of Health, Education, and Welfare.

Revised Edition, Jan.1970 pp. 28-29.

j 4.

Table of Isotopes by C.M. Lederer, J.M. Hollander, and i

I. Perlman, Sixth Edition, pa 144, 147.

l Results:

Near-surface disposal of Cm-242 exceeding 10 nCi/g would be l

~

~

acceptBle to NRC staff, if the upper concentration limit does not exceed 2 uCi/g. The concentratfor. of the daughter product l

of Cm-242, Pu-238, would,. however, need to be included in the total 10 nC1/g cumulative concentration with the other long-lived al.pha-emitting TRU nuclides in the wastes.

i i

h

2-Evaluationi In Table 1, Draft 10CFR61, an exception of TRU nuclide concentration is listed for Pu-241, a short-lived transur'anic which has a long-lived alpha-emitting daughter, Am-241.

Using the same rationale provided by Chapter 7 of the Draft Environmental Impact Statement to

. 10CFR61 (NUREG-0782, Volume 2), we calculate the ratio of the specific activity of Cm-242 to Pu-238 to be about 200. The upper concentration limit for Cm-242 is recommended to be 2 uCi/g (See Appendix I).

Furthermore, Cm-242 is a short-lived isotope (163 days). By the

[

time the 100 year institutional control period ends, any Cm-242 l

disposed of in a near surface disposal facility will be negligible.

(See' Appendix II).

b I-N Aate Calculated by Checked by

$[

Date E-Z3-F2

/ Date 2./7.Ff 82.

Approve A Lv2 9

a g

e l

l

~ ~ - -.

=_

~.

- Appendix I. (From Reference 3):

Specific Activity The rate of decay per gram or specific activity is equal to AN and f

A N = 0.693 d/T 1/2 = dis /sec/gm where T 1/2 = half-life (seconds)

N

= Number of atoms per gram A

= Decay constant (1/ seconds) i

.0 Number of atoms per gram for Cm-242 =

242.

g.

Therefore, i

NCm-242 = 2.49 x 1021 atom /g (1)

.0 Number of atoms per gram for Pu-238 =

238.

g.

Therefore, NPu-238 = 2.53 x 1021 atoms /g (2)

Since the half life of Cm-242 is 163 days (Reference 4) and the half life of Pu-238 is 86 years (Reference 4), the ratio of specific activity of Cm-242 to Pu-238 is:

0.693 x No. of atoms per gram of Cm-242 half-life (seconds) of Cm-242 0.693 x No. of atoms per gram of Pa-238 half-life (seconds) of Pu-238 Substituting (1) and (2) into equation (3), we get:

i 1

0.693 x 2.49 x 1021 (atoms /g)(365 day /yr)-

163 (days) x 86400 (sec/yr)

(4) 0.693 x 2.53 x 1021 (atoms /g) 86 (yrs) x 86400 (sec/yr)

'g,

_.,-.m

~..,,,.,. _

i i

Reducing equation (4) yields:

2.49 x 1021 (atoms /g) 365 (days /yr) 86 (yr) = 190 2.53 x 1021 (atoms /g) 163 (days)

Due to the inaccuracies of measuring TRU nuclides, we round off this value to 200.

Therefore, to compute the specific activity of Cm-242 to produce 10 nCi/g of Pu-238,-

we multiply the ratio of specific activities (200) times 10 nCi/g (the long-lived TRU limit) to get 2 uCi/g for Cm-242. Therefore, a waste with 2 uCi/g of Cm-242 will decay to 10 nCi/gm of Pu-238.

4 f

r P

r l

5

,.?-

Appendix II In order to show that Cm-242 will have negligible effect after disposal, we use

, the decay equation to compute the Cm-242 activity at the time institutional control over the disposal site is assumed to be lost. We assume that the institutional control period is 100 years. Therefore, I=I e-0.693 t/T 1/2 n

where I,

= Cm-242 activity at some original time I

= Cm-242 activity after a time interval, t T1/2 = Half-life of a particular radioactive element t

= Period of decay, years After 100 years institutional control:

t

= 100 years T 1/2 of Cm-242 = 163 days I

=I e-0.693 x 100 (yr) x 365 (days /yr) 0 163 (days) h

= 4.0 x 10-68 o

Therefore, after 100 years only 4.0 x 10-68 of the initial Cm-242 activity will remain. Therefore, its activity after the institutional control period will be n:gligible assuming that only uCi amounts of Cm-242 are initially pres ent.

l e

@