Table 8.

Comparison of radiochemical results from separate samples of a largevolume soil specimen.
(Ratios are A to B sample aliquot) .4

Master log
number

240
40: 23984

241 : 23904

239 5K

2394240,

atom ratio

atom ratio

dpm/g

dpm/g

243

Pu
dpm/g

241

90

Am
dpm/g

Sr
dpm/g

Bikini soil

O01-0065-01

1.01 40.4%

1.21 42.1%

1.02 +0.8%

1.02 20.6%

1.23 42.2%

01-0088-9]

1.01 40.9

0.86049.3

1.03 40.9

1.03 40.8

0.88329.4

0.90928.6
0.98742.1

0.968t1.1%
0.99041.7

01-0111-01

0.998+0.6

1.09 42.8

1.00 +1.6

1.00 41.3

1.10 £4.4

O1-0134-32

0.98542.5

0.90 +15

0.92744.3

0.920£3.3

0.84546.5

-

01-0157-32

1.01 40.3

1.03 40.9

1,00 40.5

1.01 40.4

1.03 41.2

—_——

1.00 40.7

O1-0180-32

0.99741.1

0.93044.8

1.00 40.8

0.99840.9

0.93044.9

—_—

9.99842.4

O01-0226-32

1.01 £0.4

1.01 40.8

0.99540.5

0.99940.4

1.01 +1.0

_

01-0318-95

0,992#2.2

01-0343-90

0.99840.8

0.955+1.3

1.04 +2.2

1.04 41.9

0.99342.6

O1-0387-95

0.9844#2.2

0.99 +28

1.06 3.6

1.05 +2.4

1.1

O1-0525-71

1,01 40.8

1.16 47.4

0.95641.3

0.95941.0

O1-0548-72

0.984+3.5

1.07 46.1

1.06 44.2

01-0617-92

1.01 41.2

1.06 44,4

1,03 40.9

1.04 +0,.9

1.09 +4.5

1.0041.1%

1.0411%

1,01£4.0%

1.0144.0%

1.0411%

06-0709-32

0.99441.1%2

0.91 411%

1.01 40.9%

' Average

1.03 +4.0

0.95044.5

1.03 £2.4

0.985£2.0

0.970£3.3 0.96522.7

1.04 40.8

1.08 46.4

0.96542.6

428

0.95110.9

1.11 £7.5
—_———

1.03 $2.6

—

1.02 43.4

0.99248.6%

0.99743.22

Eneu soil
1.01 40.9%

0.92 111%

_olcl

1.01 41.9%

06-0755-32

0.978+3.8

1.05 +2.4

1.04 #2.6

_—

1.08 +6.5

06-0893-92

1.02 +1.5

——-

0.96141.4

0.97141.3

—_——

_

0.98846 .3

Average

0.99742.1%

———

1.0144.4%

1.0143.4%

—_—-

—_—_

1.0344.7%

* All results are reported to a reference time of 1 January 1975 (001.00 2, 75).

7241

signal or calculation of a detection
limit.

Wet-chemistry measurements

served two purposes:

Am concentration more accurately.

Uncertainties in self-absorption

to permit

corrections because of voids resulting

comparison of two different methods
41an,
for measuring
and for other

can limit the accuracy of 241oy

samples,

assessment via gamma spectrometry.

from settling of the soil in the

to provide greater sensitivity

for detecting

ereo than available

Thus,

from routine gamma measurement.

41

Am data

for soil samples reported via gamma

Comparison data for 52 soil samples
are presented in Table 9.

it appears that the

The mean

spectrometry may be systematically
low by about 20 percent.

Even so,

value for the MCL:LLL ratio is.

the effect of -a 20 percent bias will

1.2 + 164, with evidence for signifi-

be negligible on the estimated exter-

cant bias.

nal dose since

For soil samples, wet

very small fraction to the total.

chemistry is expected to assess the
~16-

a]

J010098

Lam contributed a

Select target paragraph3