Boris E. Burakov

Dr. Boris E. Burakov

V.G. Khlopin Radium Institute, St. Peterburg 194021, Russia
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Research Focus & Metrics

Academic Career Length

23Years (2004-Present)

(Calculated once Scilit publication data is synced: current year − year of first publication + 1)

Representative Publications

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1 January 2004 in MRS Proceedings
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Boris E. BurakovBoris E. Burakov
Boris E. Burakov
MYMaria A. Yagovkina
Maria A. Yagovkina
VGVladimir M. Garbuzov
Vladimir M. Garbuzov
AKAlexander A. Kitsay
Alexander A. Kitsay
VZVladimir A. Zirlin
Vladimir A. Zirlin

23 July 2020 in Challenges
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Bella ZubekhinaBella Zubekhina
Bella Zubekhina
Boris E. BurakovBoris E. Burakov
Boris E. Burakov
Michael I. OjovanMichael I. Ojovan
Michael I. Ojovan
We examined the degradation of nuclear waste borosilicate and phosphate glasses containing strong alpha-emitter 238Pu at a specific activity of 6.33 × 105 MBq/g in comparison with similar non-radioactive, non-radioactive irradiated and radioactive samples containing beta- and gamma-emitters, namely radionuclides 134Cs and 137Cs. For irradiation and leaching experiments, we used borosilicate and phosphate glasses, which are well-known and currently used to immobilize high-level radioactive waste. The main focus was the observation of the surface of altered glasses. Comparative analysis of hydrolytic surface alteration of borosilicate and phosphate nuclear waste glasses reveals that the behavior of radioactive samples differs significantly from that of non-radioactive glasses.

21 January 2021 in Sustainability
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BZBella Zubekhina
Bella Zubekhina
Boris E. BurakovBoris E. Burakov
Boris E. Burakov
ESEkaterina Silanteva
Ekaterina Silanteva
YPYuri Petrov
Yuri Petrov
VYVasily O. Yapaskurt
Vasily O. Yapaskurt
DDDmitry Danilovich
Dmitry Danilovich
Samples of Chernobyl fuel debris, including massive corium and “lava” were collected inside the Chernobyl “Sarcophagus” or “Shelter” in 1990, transported to Leningrad (St. Petersburg) and stored under laboratory conditions for many years. In 2011 aged samples were visually re-examined and it was confirmed that most of them remained intact, although some evidence of self-destruction and chemical alteration were clearly observed. Selected samples of corium and “lava” were affected by static leaching at temperatures of 25, 90 and 150 °C in distilled water. A normalized Pu mass loss (NLPu) from corium samples after 140 days was noted to be 0.5 g/m2 at 25 °C and 1.1 g/m2 at 90 °C. For “lava” samples NLPu was 2.2–2.3 g/m2 at 90 °C for 140 days. The formation of secondary uranyl phases on the surface of corium and “lava” samples altered at 150 °C was confirmed. The results obtained are considered as an important basis for the simulation of fuel debris aging at Fukushima Daiichi nuclear power plant (NPP).

1 October 2021 in Materials Research Bulletin
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MZM.V. Zamoryanskaya
M.V. Zamoryanskaya
EDE.V. Dementeva
E.V. Dementeva
KOKseniia Orekhova
Kseniia Orekhova
VKV.A. Kravets
V.A. Kravets
ATA.N. Trofimov
A.N. Trofimov
Boris E. BurakovBoris E. Burakov
Boris E. Burakov

24 January 2021 in Sustainability
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PMPolina Mikhailova
Polina Mikhailova
Boris E. BurakovBoris E. Burakov
Boris E. Burakov
NENikolai Eremin
Nikolai Eremin
АААлексей Аверин
Алексей Аверин
ASAndrey A. Shiryaev
Andrey A. Shiryaev
The paper consists of two main parts: a microscopic and spectroscopic investigation of the single crystal of 17-year-old 238Pu-doped Eu-monazite, and a theoretical calculation of the properties of several structural types of orthophosphates. It is shown that actinide-doped monazite is prone to the formation of mechanically weak, poorly crystalline crust, presumably consisting of rhabdophane. Its formation is likely promoted by the formation of peroxides and, potentially, acidic compounds, due to the radiolysis of atmospheric moisture. The calculations of mixing the enthalpies and Gibbs energies of binary solid solutions of Pu and rare earth element (REE) phosphates that were performed for the principal structural types—monazite, xenotime, rhabdophane—show that, in the case of light REEs, the plutonium admixture is preferentially redistributed into the rhabdophane. This process strongly affects the behavior of actinides, leached from a monazite-based waste form. The applications of these results for the development of actinide waste forms are discussed. The current data on the behavior of real actinide-doped monazite suggest that this type of ceramic waste form is not very resistant, even in relatively short time periods.

1 January 2004 in MRS Proceedings
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Journal Article
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JHJohn M. Hanchar
John M. Hanchar
Boris E. BurakovBoris E. Burakov
Boris E. Burakov
MZMaria V. Zamoryanskaya
Maria V. Zamoryanskaya
VGVladimir M. Garbuzov
Vladimir M. Garbuzov
AKAlexander A. Kitsay
Alexander A. Kitsay
VZVladimir A. Zirlin
Vladimir A. Zirlin