Lake Michigan environmental survey : final report / [edited] by John C. Ayers.

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

/ 117
Pages

Actions

file_download Download Options Download this page PDF - Page 32 Image - Page 32 Plain Text - Page 32 Download this item Item PDF - Pages #1-117

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

Link to this Item
https://name.umdl.umich.edu/4738400.0001.001
Link to this scan
https://quod.lib.umich.edu/g/glrr/4738400.0001.001/44

Rights and Permissions

The University of Michigan Library provides access to these materials for educational and research purposes. These materials may be protected by copyright. If you decide to use any of these materials, you are responsible for making your own legal assessment and securing any necessary permission.

Manifest
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.
Do you have questions about this content? Need to report a problem? Please contact us.

Downloading...

Download PDF Cancel