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Titlebook: Actinide Speciation in High Ionic Strength Media; Experimental and Mod Donald T. Reed,Sue B. Clark,Linfeng Rao Book 1999 Springer Science+B

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https://doi.org/10.1007/978-3-642-50778-6ed temperatures, and the materials used in the encapsulation, backfill, etc. By contrast, the behavior in the far field should resemble a more normal environmental situation. The difference in the nature of the data base required for satisfactory modeling of radionuclide migration in these two situa
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https://doi.org/10.1007/978-3-642-50778-6the main technical parts of the installations slated for controlled decommissioning or is contained by methods not totally reliable for long-term storage. Large cleanup programs are already under way in the U.S. for former nuclear sites (USDOE, 1989; USDOE, 1990). Other areas contaminated by nuclear
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Zusammenfassung der Untersuchungsergebnisse,alues of pH, composition, ionic strength, temperature, and pressure. The solubility of these elements in natural waters can be determined experimentally or by modeling. Since direct measurements are not presently available for many metals of interest, it is important to develop methods that can be u
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Frank Bickenbach,Lars Kumkar,Hartmut Wolfin 177 large (mostly 4 million liter capacity) underground concrete tanks with steel liners. The wastes consist of processing chemicals, cladding chemicals, fission products, and actinides. Waste solutions from chemical processing facilities were made alkaline by adding sodium hydroxide before sendi
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Zusammenfassung der Untersuchungsergebnisse,d to serve as permanent repositories for transuranic waste. Safety assessment required for the licensing of these sites necessitates the modeling of potential radionuclide releases from proposed nuclear waste repositories and the estimation of actinide solubilities in surrounding groundwaters. An un
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Signalauswertung und Kalibrierung,etic brines under different partial pressures of CO.. The stable solid phase in solutions containing concentrated NaCl (2 m and 4 m)/Na.CO. (0.1 to 2.0 m) and NaCl (2 m)/NaHCO. (0.1 to 1.0 m) was identified by X-ray diffraction to be NaNd(CO.)..6H.O(c), which is the same equilibrium solid phase prev
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Signalauswertung und Kalibrierung,y basic solution of sodium nitrate, nitrite, and aluminate at mole/L levels and sodium carbonate, sulfate, chloride, etc. at 0.1 M to 10. M or less. Plutonium is present at a 10. to 10. α d/min-mL level; the radiation level of the solution is about 4 × 10. R/hr from .Cs γ-rays. To conserve space in
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