7.l. Radiochemical Analysis and Radioactivity Measurements




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.

TABLE 7.1

Detection Limits

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.

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.

TABLE 7.2

Summary of DOE-EML-QAP Samples, 1995

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.

a A hyphen indicates that a sample is not required for analysis.



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