<p><i>Background:</i> The operation of radioactive waste (RAW) pools is associated with potential environmental risks. Remediation of adjacent territories represents a&#xa0;priority in the Strategy for Environmental Safety of the Russian Federation.</p><p><i>Aim:</i> To determine the characteristics of a&#xa0;biogeochemical anti-migration barrier created for the remediation of aquifers with complex contamination, as well as to assess the effectiveness of this barrier.</p><p><i>Materials and methods:</i> The elemental composition of samples was determined by inductively coupled plasma mass spectrometry (ICP-MS); the method of capillary gel electrophoresis (CGE) was used to determine the ion concentration.</p><p><i>Results and discussion:</i> Maximum concentrations of ammonium, sulfates, uranium, and nitrates in RAW filtration zones are 448, 1800, 4.9, and 10,000 mg/L, respectively. As a&#xa0;result of bioremediation, iron partially passes into sulfide phases, while the remained iron re-precipitates into hydroxide phases during bio- or reoxidation. Purification yielded a&#xa0;chemically active mineral sediment preventing the spread of&#xa0;U, Np, Pu, and Tc redox-sensitive radionuclides, as well as Sr and Am.</p><p><i>Conclusion:</i> An effective and economically feasible approach to the purification of groundwater near nuclear fuel cycle facilities during their operation and post-mothballing periods has been tested. The tested method involves the <i>in situ </i>intensification of microbial processes by introducing soluble sources of organic carbon and phosphorus.</p>

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Experience of creating an in situ biogeochemical barrier in contaminated groundwater at nuclear fuel cycle facilities. part 1

  • G. D. Artemyev,
  • A. V. Safonov,
  • A. A. Zubkov,
  • Ivan Y. Myasnikov,
  • A. P. Novikov

摘要

Background: The operation of radioactive waste (RAW) pools is associated with potential environmental risks. Remediation of adjacent territories represents a priority in the Strategy for Environmental Safety of the Russian Federation.

Aim: To determine the characteristics of a biogeochemical anti-migration barrier created for the remediation of aquifers with complex contamination, as well as to assess the effectiveness of this barrier.

Materials and methods: The elemental composition of samples was determined by inductively coupled plasma mass spectrometry (ICP-MS); the method of capillary gel electrophoresis (CGE) was used to determine the ion concentration.

Results and discussion: Maximum concentrations of ammonium, sulfates, uranium, and nitrates in RAW filtration zones are 448, 1800, 4.9, and 10,000 mg/L, respectively. As a result of bioremediation, iron partially passes into sulfide phases, while the remained iron re-precipitates into hydroxide phases during bio- or reoxidation. Purification yielded a chemically active mineral sediment preventing the spread of U, Np, Pu, and Tc redox-sensitive radionuclides, as well as Sr and Am.

Conclusion: An effective and economically feasible approach to the purification of groundwater near nuclear fuel cycle facilities during their operation and post-mothballing periods has been tested. The tested method involves the in situ intensification of microbial processes by introducing soluble sources of organic carbon and phosphorus.