Hostname: page-component-586b7cd67f-vdxz6 Total loading time: 0 Render date: 2024-11-22T20:56:31.713Z Has data issue: false hasContentIssue false

Determination of the secondary phases at the acidic LNW disposal

Published online by Cambridge University Press:  20 February 2017

Irina Vlasova*
Affiliation:
Department of Chemistry, Lomonosov Moscow State University, Moscow, Russia
Anna Romanchuk
Affiliation:
Department of Chemistry, Lomonosov Moscow State University, Moscow, Russia
Anna Volkova
Affiliation:
Frumkin Institute of Physical chemistry and Electrochemistry RAS, Moscow, Russia
Elena Zakharova
Affiliation:
Frumkin Institute of Physical chemistry and Electrochemistry RAS, Moscow, Russia
Igor Presnyakov
Affiliation:
Department of Chemistry, Lomonosov Moscow State University, Moscow, Russia
Alexey Sobolev
Affiliation:
Frumkin Institute of Physical chemistry and Electrochemistry RAS, Moscow, Russia
Stepan Kalmykov
Affiliation:
Department of Chemistry, Lomonosov Moscow State University, Moscow, Russia
*
Get access

Abstract

The migration behavior of the long-lived actinides was studied under the conditions of the deep disposal of the acidic liquid nuclear waste (LNW). Composition of LNW varies significantly including acidic technological wastes (pH ∼2.4), which consist of sodium nitrate, acetic acid, corrosion products (Fe, Cr, Mn, Ni, Al), fission products and actinides. Corrosion products tend to precipitate under the LNW disposal conditions that favor forming of the phases with high sorption capacity towards actinides. Sands of reservoir bed have their own initial sorbent surfaces besides new secondary phases that have formed as a result of interaction with acidic LNW. The nearest to the injection well conditions are gradually changing from pH ∼2.4 till neutral values due to the dilution by groundwater with formation of new precipitated phases of corrosion products. The solid phases characterization is a necessary step on the path of knowledge of migration behavior of actinides. The secondary phases of both corrosion products and sands of reservoir bed under LNW disposal conditions were characterized using XRD, SEM and Mössbauer spectroscopy. The recent results of the analyses of the behavior of actinides (Pu. U, Np, Am) under the conditions of the injection of the acid LNW are presented in the paper.

Type
Articles
Copyright
Copyright © Materials Research Society 2017 

Access options

Get access to the full version of this content by using one of the access options below. (Log in options will check for institutional or personal access. Content may require purchase if you do not have access.)

References

REFERENCES

Spitsyn, V.I., Pimenov, M.K., Balukova, V.D. et al. Principal prerequisites and practice of using deep aquifers for burial of liquid radioactive wastes. Atomnaya Energiya., 44, 3, 161168 (1978).Google Scholar
Rybalchenko, A.I., Pimenov, M.K., Kostin, P.P. et al. Deep burial of the liquid radioactive wastes. Moscow IzdAT, 256 p. (1994) In Russian.Google Scholar
Rybalchenko, A.I., Pimenov, M.K., Kurochkin, V.M., Kamnev, E.N., Korotkevich, V.M., Zubkov, A.A. and Khafizov, R.R.. Deep Injection Disposal of Liquid Radioactive Waste in Russia, 1963–2002: Results and Consequences. Developments in Water Science, 52, 1319 (2005).Google Scholar
Noskov, M.D.; Istomin, A.D.; Kesler, A.G.; Zubkov, A.A.; Zakharova, E.V.; Egorov, G.F. Simulation of the distribution of radionuclides in the reservoir bed for deep-well injection disposal of acid liquid radioactive waste. Radiokhimiya; v. 49(2); p. 182187 (2007)Google Scholar
Zubkov, A.A., Danilov, V.V., Istomin, A.D., Noskov, M.D. Prognostic modeling of the liquid radioactive wastes filtrate distribution within the deep underground disposal of the Siberian chemical combine. Tomsk State University Journal. № 306, 161168. (2008) In Russian.Google Scholar
Zakharova, E.V., Kaimin, E.P., Darskaya, E.N. et al. Physicochemical processes occurring in long-term storage of Liquid Radioactive Waste in Deep underground collector beds. Radiokhimiya 43, 378380 (2001).Google Scholar
Zakharova, E.V., Darskaya, E.N., Kaimin, E.P. et al. Effect of contact time of Liquid Radioactive Waste with bed rock of Underground Repository on migration behavior of 90Sr, 137Cs, 239Pu and 241Am. Radiokhimiya 45, 282284 (2003).Google Scholar
Vlasova, I.E., Zakharova, E.V., Volkova, A.G., Averin, A.A., Kalmykov, S.N. Effect of Corrosion Products on the Pu Speciation in Rocks of Reservoir Horizon in Interaction with Acidic Solutions under Hydrothermal Conditions. Радиохимия, 56, 2, 176183 (2014).Google Scholar
Kalmykov, S.N., Vlasova, I.E., Romanchuk, A.Yu, Zakharova, E.V., Volkova, A.G., Presnyakov, I.A. Partitioning and speciation of Pu in the sedimentary rocks aquifer from the deep liquid nuclear waste disposal. Radiochimica Acta, 103, 3, 175185 (2015).Google Scholar
Matsnev, M.E., Rusakov, V.S. SpectrRelax: An Application for Mössbauer Spectra Modeling and Fitting. // AIP Conf. Proc., 1489, P.178 (2012).Google Scholar
Menil, F. Systematic trends of the 57Fe Moessbauer isomer shifts in (FeOn) and (FeFn) polyhedra. Evidence of a new correlation between the isomer shift and the inductive effect of the competing bond T-X (-Fe) (where X is O or F and T any element with a formal positive charge). J. Phys. Chem. Solids 46, 763 (1985).Google Scholar
Pan, Y., Zhu, R. and Ping, J. Mineralogical alteration of thermally treated siderite in air: Moessbauer spectroscopy results. Chinese Science Bulletin, 44, 18, 17121717 (1999).Google Scholar