Lake Michigan environmental survey : final report / [edited] by John C. Ayers.
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Five planchets were prepared for each of the radioisotopes in Table A-15 with the exception of Cs-137; three Cs-137 planchets were prepared. The calibration planchets were prepared as follows: 1. One milliliter of a wetting agent was placed in the planchet to insure uniform drying. Without the wetting agent the surface tension of any liquid in the planchet would pull the last few drops to the side of the planchet which would result in a ring source instead of a circular source. The wetting agent used was Kodak Photo-Flo 200, diluted 1:100 with water. 2. The standard solutions were transferred by weight from the polyethylene bottles to the planchets. The transfer was done using glass eye droppers which had been treated with Siliclad to minimize adsorption of the radioactive ions on the glass. The planchet was swirled carefully to insure that the radioactivity was dispersed uniformly across the planchet. 3. The planchet was placed under a heat lamp in a hood, and the liquid was evaporated to dryness. 4. One milliliter of a sealer was transferred to the planchet and evaporated to dryness. The sealer consisted of 0.5 grams of plexiglass powder dissolved in 100 milliliters of 1, 2-dichloroethane. Constant Counting Conditions. It is very important that the calibration planchets be counted under the same conditions as the sample planchets. Parameters such as temperature can be kept constant by following good laboratory practice, e.g. keeping the windows and door to the counting room closed at all times. Contamination of the detector must be avoided. The gain and zero settings of the equipment must be constant while counting calibration planchets. However, the spectrum analysis computer program can make the necessary corrections if the gain and zero settings of an environmental sample differ from the calibration gain and zero settings. In order to determine how large the activity of a calibration planchet could be before induced gain shifts and live timer errors become significant, two experiments were conducted. In both experiments the percent dead time of the spectrometer was used as a measure of the activity of the sample being counted. The first experiment determined the effect of sample activity on induced gain shifts. This was done by building a tower of 5 cm diameter, 1.5 cm tall A-32
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About this Item
- Title
- Lake Michigan environmental survey : final report / [edited] by John C. Ayers.
- Author
- Ayers, John C. (John Carr), 1912-
- Canvas
- Page 32
- Publication
- Ann Arbor, Mich. :: University of Michigan, Great Lakes Research Division,
- 1970.
- Subject terms
- Radioecology -- Michigan, Lake.
- Michigan, Lake.
Technical Details
- Collection
- Great Lakes Digital Library
- Link to this Item
-
https://name.umdl.umich.edu/4738400.0001.001
- Link to this scan
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https://quod.lib.umich.edu/g/glrr/4738400.0001.001/44
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- Manifest
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https://quod.lib.umich.edu/cgi/t/text/api/manifest/glrr:4738400.0001.001
Cite this Item
- Full citation
-
"Lake Michigan environmental survey : final report / [edited] by John C. Ayers." In the digital collection Great Lakes Digital Library. https://name.umdl.umich.edu/4738400.0001.001. University of Michigan Library Digital Collections. Accessed May 17, 2025.