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131210e19801101nmu ot f0|||||eng|d |
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20230817214413.6 |
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|a (TOE)ost6669598
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| 035 |
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|a (TOE)6669598
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|a TOE
|c TOE
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|a GDWR
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|a 54
|2 edbsc
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|a 12
|2 edbsc
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|a E 1.99:sand-80-1064
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| 088 |
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|a sand-80-1064
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| 245 |
0 |
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|a Sorption coefficients for radionuclides on samples from the water-bearing Magenta and Culebra members of the Rustler Formation
|h [electronic resource]
|
| 260 |
|
|
|a Albuquerque, N.M. :
|b Sandia National Laboratories. ;
|a Oak Ridge, Tenn. :
|b distributed by the Office of Scientific and Technical Information, U.S. Dept. of Energy,
|c 1980.
|
| 300 |
|
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|a Pages: 23 :
|b digital, PDF file.
|
| 336 |
|
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|a text
|b txt
|2 rdacontent.
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| 337 |
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|a computer
|b c
|2 rdamedia.
|
| 338 |
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|a online resource
|b cr
|2 rdacarrier.
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| 500 |
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|a Published through SciTech Connect.
|
| 500 |
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|a 11/01/1980.
|
| 500 |
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|a "sand-80-1064"
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| 500 |
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|a Lynch, A. W.; Dosch, R. G.
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| 520 |
3 |
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|a The sorbing characteristics of samples from the Magenta and Culebra dolomites of the Rustler Formation (which overlie the proposed site for the Waste Isolation Pilot Plant (WIPP) in southeastern New Mexico) for various radionuclides have been studied. Core samples extracted from various depths and boreholes within a given formation were selected to provide a cross section of materials which are present in the formations. They varied in composition from pure dolomite to nearly pure anhydrite. The radionuclides used in the sorption coefficient measurements (isotopes of Cs, Sr, Tc, Eu, Am and Pu) were dissolved in a simulated Culebra groundwater at concentrations of 0.1 ..mu..Ci/m1 or less. The results indicate that the sorption coefficients (Kd's) of these water-bearing units may vary widely depending on the borehole area and over several feet in depth in a common borehole. Cesium Kd values from 0.6 to 218 ml/g and 1.2 to 68 on Magenta and Culebra samples, respectively. Strontium Kd values ranged from 1.1 to 30 on Magenta Samples and from 0.6 to 32 on Culebra samples. Variations of Eu, Pu and Am Kd's were generally less than an order of magnitude on both Culebra and Magenta samples. Technetium was not sorbed by any of the samples. With few exceptions, samples with high dolomite contents had higher sorption coefficients than those with high anhydrite concentrations. Clay content may also be a factor for some radionuclides, particularly Cs, which has been shown to sorb preferentially on clay particles in Magenta.
|
| 536 |
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|b AC04-76DP00789.
|
| 650 |
|
7 |
|a Information.
|2 local.
|
| 650 |
|
7 |
|a Beta Decay Radioisotopes.
|2 local.
|
| 650 |
|
7 |
|a Experimental Data.
|2 local.
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| 650 |
|
7 |
|a Heavy Nuclei.
|2 local.
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| 650 |
|
7 |
|a Functional Models.
|2 local.
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| 650 |
|
7 |
|a Environmental Transport.
|2 local.
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| 650 |
|
7 |
|a Even-even Nuclei.
|2 local.
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| 650 |
|
7 |
|a Cesium 137.
|2 local.
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| 650 |
|
7 |
|a Electron Capture Radioisotopes.
|2 local.
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| 650 |
|
7 |
|a Sulfur Compounds.
|2 local.
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| 650 |
|
7 |
|a Isotopes.
|2 local.
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| 650 |
|
7 |
|a Water.
|2 local.
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| 650 |
|
7 |
|a New Mexico.
|2 local.
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| 650 |
|
7 |
|a Carbonates.
|2 local.
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| 650 |
|
7 |
|a Anhydrite.
|2 local.
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| 650 |
|
7 |
|a Southwest Region.
|2 local.
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| 650 |
|
7 |
|a Magnesium Compounds.
|2 local.
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| 650 |
|
7 |
|a Underground Disposal.
|2 local.
|
| 650 |
|
7 |
|a Calcium Compounds.
|2 local.
|
| 650 |
|
7 |
|a Sorption.
|2 local.
|
| 650 |
|
7 |
|a Pilot Plants.
|2 local.
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| 650 |
|
7 |
|a Strontium 85.
|2 local.
|
| 650 |
|
7 |
|a Isomeric Transition Isotopes.
|2 local.
|
| 650 |
|
7 |
|a Beta-plus Decay Radioisotopes.
|2 local.
|
| 650 |
|
7 |
|a Numerical Data.
|2 local.
|
| 650 |
|
7 |
|a Salt Deposits.
|2 local.
|
| 650 |
|
7 |
|a Boreholes.
|2 local.
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| 650 |
|
7 |
|a Plutonium 238.
|2 local.
|
| 650 |
|
7 |
|a Waste Management.
|2 local.
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| 650 |
|
7 |
|a Cavities.
|2 local.
|
| 650 |
|
7 |
|a Technetium Isotopes.
|2 local.
|
| 650 |
|
7 |
|a Calcium Sulfates.
|2 local.
|
| 650 |
|
7 |
|a Americium 243.
|2 local.
|
| 650 |
|
7 |
|a Sorptive Properties.
|2 local.
|
| 650 |
|
7 |
|a Hydrogen Compounds.
|2 local.
|
| 650 |
|
7 |
|a Radioisotopes.
|2 local.
|
| 650 |
|
7 |
|a Radionuclide Migration.
|2 local.
|
| 650 |
|
7 |
|a Days Living Radioisotopes.
|2 local.
|
| 650 |
|
7 |
|a Mass Transfer.
|2 local.
|
| 650 |
|
7 |
|a Plutonium Isotopes.
|2 local.
|
| 650 |
|
7 |
|a Alkaline Earth Isotopes.
|2 local.
|
| 650 |
|
7 |
|a Rocks.
|2 local.
|
| 650 |
|
7 |
|a Beta-minus Decay Radioisotopes.
|2 local.
|
| 650 |
|
7 |
|a Geologic Deposits.
|2 local.
|
| 650 |
|
7 |
|a Carbonate Rocks.
|2 local.
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| 650 |
|
7 |
|a Ground Water.
|2 local.
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| 650 |
|
7 |
|a Actinide Isotopes.
|2 local.
|
| 650 |
|
7 |
|a Radioactive Waste Disposal.
|2 local.
|
| 650 |
|
7 |
|a Even-odd Nuclei.
|2 local.
|
| 650 |
|
7 |
|a Waste Disposal.
|2 local.
|
| 650 |
|
7 |
|a Rare Earth Nuclei.
|2 local.
|
| 650 |
|
7 |
|a Oxygen Compounds.
|2 local.
|
| 650 |
|
7 |
|a Carbon Compounds.
|2 local.
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| 650 |
|
7 |
|a Dolomite.
|2 local.
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| 650 |
|
7 |
|a Minerals.
|2 local.
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| 650 |
|
7 |
|a Magnesium Carbonates.
|2 local.
|
| 650 |
|
7 |
|a Europium Isotopes.
|2 local.
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| 650 |
|
7 |
|a Surface Properties.
|2 local.
|
| 650 |
|
7 |
|a Management.
|2 local.
|
| 650 |
|
7 |
|a Intermediate Mass Nuclei.
|2 local.
|
| 650 |
|
7 |
|a Americium Isotopes.
|2 local.
|
| 650 |
|
7 |
|a Odd-even Nuclei.
|2 local.
|
| 650 |
|
7 |
|a Drill Cores.
|2 local.
|
| 650 |
|
7 |
|a Alkali Metal Isotopes.
|2 local.
|
| 650 |
|
7 |
|a Odd-odd Nuclei.
|2 local.
|
| 650 |
|
7 |
|a Cesium Isotopes.
|2 local.
|
| 650 |
|
7 |
|a Sulfates.
|2 local.
|
| 650 |
|
7 |
|a Strontium Isotopes.
|2 local.
|
| 650 |
|
7 |
|a Europium 152.
|2 local.
|
| 650 |
|
7 |
|a Actinide Nuclei.
|2 local.
|
| 650 |
|
7 |
|a Usa.
|2 local.
|
| 650 |
|
7 |
|a North America.
|2 local.
|
| 650 |
|
7 |
|a Alkaline Earth Metal Compounds.
|2 local.
|
| 650 |
|
7 |
|a Rare Earth Isotopes.
|2 local.
|
| 650 |
|
7 |
|a Sedimentary Rocks.
|2 local.
|
| 650 |
|
7 |
|a Alpha Decay Radioisotopes.
|2 local.
|
| 650 |
|
7 |
|a Nuclei.
|2 local.
|
| 650 |
|
7 |
|a Data.
|2 local.
|
| 650 |
|
7 |
|a Technetium 99.
|2 local.
|
| 650 |
|
7 |
|a Years Living Radioisotopes.
|2 local.
|
| 650 |
|
7 |
|a Hours Living Radioisotopes.
|2 local.
|
| 650 |
|
7 |
|a Management Of Radioactive And Non-radioactive Wastes From Nuclear Facilities.
|2 edbsc.
|
| 650 |
|
7 |
|a Environmental Sciences.
|2 edbsc.
|
| 710 |
2 |
|
|a Sandia National Laboratories.
|4 res.
|
| 710 |
1 |
|
|a United States.
|b Department of Energy.
|b Office of Scientific and Technical Information.
|4 dst.
|
| 856 |
4 |
0 |
|u http://www.osti.gov/servlets/purl/6669598/
|z Online Access
|
| 907 |
|
|
|a .b76299582
|b 03-07-23
|c 12-11-13
|
| 998 |
|
|
|a web
|b 12-11-13
|c f
|d m
|e p
|f eng
|g nmu
|h 0
|i 2
|
| 956 |
|
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|a Information bridge
|
| 999 |
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|i 6adc6ac2-905a-58ea-a132-f5fde8790293
|s 1163379a-b322-599d-906a-de394105bba6
|
| 952 |
f |
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|p Can circulate
|a University of Colorado Boulder
|b Online
|c Online
|d Online
|e E 1.99:sand-80-1064
|h Superintendent of Documents classification
|i web
|n 1
|
