By Horst Geckeis, Thomas Rabung, Thorsten Schäfer (auth.), Stepan N. Kalmykov, Melissa A. Denecke (eds.)
This is the 1st publication to hide actinide nano learn. it's of curiosity either for primary examine into the chemistry and physics of f-block parts in addition to for utilized researchers similar to these learning the long term protection of nuclear waste disposal and constructing remediation ideas. The authors conceal very important problems with the formation of actinide nano-particles, their houses and constitution, environmental habit of colloids and nanoparticles on the topic of the secure disposal of nuclear wastes, modeling and complex tools of characterization on the nano-scale.
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Extra info for Actinide Nanoparticle Research
Kim J. I. (2006) Significance of actinide chemistry for the long-term safety of waste disposal. Nuclear Engineering and Technology 38, 459–482. Kim J. I. and Czerwinski K. R. (1996) Complexation of metal ions with humic acid: Metal ion charge neutralization model. Radiochimica Acta 73, 5–10. Kim J. , and Lux D. (1984) Colloid generation and the actinide migration in Gorleben groundwaters. Materials Research Society Symposium Proceedings 26, 31–40. Kim J. , Li G. , and Psarros N. (1990) Characterization of humic and fulvic-acids from Gorleben groundwater.
Acknowledgments Part of the studies described here were funded by the Federal Ministry of Economics and Technology (BMWi) under the joint KIT-INE, GRS research project “KOLLORADO & KOLLORADO 2” and the SKB/KTH “Colloid project”. We also want to thank all organizations contributing to the funding of the Colloid Formation and Migration (CFM) project, namely: ANDRA (France), BMWi (Germany), JAEA (Japan), CRIEPI (Japan), AIST (Japan), NAGRA (Switzerland), POSIVA (Finland) and SKB (Sweden). , and Lopez-Torrubia T.
2009). A clear quantitative assessment of colloid mediated actinide migration under given conditions in contaminated sites or in any water intrusion scenario for a high level nuclear waste repository is, however, still not possible (Honeyman 1999). , high flow rate water sampling (Puls et al. 1990) or artifacts of sampling (Buesseler et al. 2003; Kaplan et al. 1993; Ryan and Gschwend 1990) may counterfeit their existence. Re-suspension of larger actinide containing particulate matter is relevant in contaminated surface water, but hard to quantify and to predict, and certainly less relevant in deep ground water.