All nuclear instrumentation is calibrated with standard sources obtained from or traceable to the
NIST. The equipment is usually checked daily with secondary counting standards to ensure
proper operation. Samples are periodically analyzed in duplicate or with the addition of known
amounts of a radionuclide to check precision and accuracy. When a nuclide was not detected, the
result is given as "less than" (<) the detection limit by the analytical method used. The detection
limits were chosen so that the measurement uncertainty at the 95% confidence level is equal to
the measured value. The air and water detection limits for all radionuclides for which
measurements were made are given in Table 7.1. The relative error in a result decreases with
increasing concentration. At a concentration equal to twice the detection limit, the error is about
50% of the measured value and at 10 times the detection limit, the error is about 10%.
Average values are usually accompanied by a plus-or-minus () limit value. Unless otherwise stated, this value is the standard error at the 95% confidence level calculated from the standard deviation of the average. The limit value is a measure of the range in the concentrations encountered at that location; it does not represent the conventional uncertainty in the average of repeated measurements on the same or identical samples. Since many of the variations observed in environmental radioactivity are not random but occur for specific reasons (e.g., seasonal variations), samples collected from the same location at different times are not replicates. The more random the variation in activity at a particular location, the closer the confidence limits will represent the actual distribution of values at that location. The averages and confidence limits should be interpreted with this in mind. When a plus-or-minus value accompanies an individual result in this report, it represents the statistical counting error at the 95% confidence level.
Detection Limits Participation continued in the DOE Environmental Measurements Laboratory Quality Assurance
Program (DOE-EML-QAP), a semiannual distribution of four different sample matrices
containing various combinations of radionuclides that are analyzed. Table 7.2 summarizes the
results for 1995. In the table, the Environmental Measurements Laboratory (EML) value, which
is the result of duplicate determinations by that laboratory, is compared with the average value
obtained in the ANL-E laboratory. Information that will assist in judging the quality of the
results includes the fact that typical uncertainties for ANL-E's analyses are 2 to 50%, and that the
uncertainties in the EML results are 1 to 30% (depending on the nuclide and the amount present).
For most analyses for which the differences are large (> 20%), the concentrations were quite low
and the differences were within the measurement uncertainties.
Summary of DOE-EML-QAP Samples, 1995 a A hyphen indicates that a sample is not required for analysis.
TABLE 7.1
Nuclide or
Activity
Air
(fCi/m3)
Water
(pCi/L)
Americium-241
-a
0.001
Beryllium-7
5
-
Californium-249
-
0.001
Californium-252
-
0.001
Cesium-137
0.1
1
Curium-242
-
0.001
Curium-244
-
0.001
Hydrogen-3
100
100
Lead-210
1
-
Neptunium-237
-
0.001
Plutonium-238
0.0003
0.001
Plutonium-239
0.0003
0.001
Radium-226
-
0.1
Radium-228
-
0.1
Strontium-89
0.1
2
Strontium-90
0.01
0.25
Thorium-228
0.001
-
Thorium-230
0.001
-
Thorium-232
0.001
-
Uranium-234
0.0003
0.01
Uranium-235
0.0003
0.01
Uranium-238
0.0003
0.01
Uranium -
natural
0.02
0.2
Alpha
0.2
0.2
Beta
0.5
1
a A hyphen indicates that a value is not
required.
TABLE 7.2
Percent Difference From EML Value
Radionuclide
Air Filters
Soil
Vegetation
Water
Hydrogen-3
-a
-
-
15 (2)
Potassium-40
-
10 (2)
13 (2)
-
Manganese-54
13 (2)
-
-
11 (2)
Cobalt-57
22 (2)
-
-
-
Cobalt-60
10 (2)
-
14 (2)
13 (2)
Strontium-90
4 (2)
13 (2)
6 (2)
1 (2)
Ruthenium-106
16 (1)
-
-
-
Antimony-125
10 (2)
-
-
-
Cesium-134
3 (1)
-
-
13 (2)
Cesium-137
13 (2)
11 (2)
21 (2)
12 (2)
Cerium-144
24 (2)
-
-
21 (1)
Uranium-234
12 (2)
8 (2)
-
10 (2)
Uranium-238
22 (2)
1 (2)
-
17 (2)
Plutonium-238
2 (2)
3 (2)
9 (1)
2 (2)
Plutonium-239
13 (2)
6 (2)
14 (2)
13 (2)
Americium-241
4 (2)
20 (2)
12 (2)
5 (2)
Note: The value in parentheses is the number of samples.
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