Technetium Retention and Remobilization Potential after Prolonged Reaction in Fe(III)- and Sulfate-Reducing Model Aquifer Systems

<sup>99</sup>Tc is a long-lived radioactive fission product whose subsurface mobility is governed by redox conditions. Under oxic conditions, soluble Tc(VII)O<sub>4</sub><sup>-</sup> is mobile, whereas under reducing conditions, poorly soluble Tc(IV) phases limit transport. Microcosm studies have frequently reported TcO<sub>2</sub>-like solids and, less consistently, Tc(IV)-sulfides. The stability of Tc(IV)-sulfides under environmentally relevant conditions remains unclear. Here, we used flowing sediment columns representative of the Sellafield subsurface to examine Tc speciation and stability over ∼1 year. Under reducing conditions, >90% of added TcO<sub>4</sub><sup>-</sup> (400 μg) was retained under both Fe(III)- and sulfate-reducing conditions. X-ray absorption spectroscopy showed TcO<sub>2</sub>-like phases dominated in Fe(III)-reducing columns, while Tc(IV)-sulfides dominated after sustained sulfate reduction. Sequential extractions indicated that Tc in sulfidic sediments was more recalcitrant (≤23% released by weak acids) than in Fe(III)-reducing systems (∼60% released). With oxic groundwater pumping, effluent Tc sourced from the sediments rose rapidly. Over 160 days, the sulfidic columns remobilized ∼25% of their Tc inventory compared to ∼50% in Fe(III)-reducing columns. The Tc(IV)-sulfides also gradually oxidized to form TcO<sub>2</sub> phases. While Tc(IV)-sulfides may enhance Tc retention under reducing conditions, TcO<sub>2</sub> phases more likely govern <sup>99</sup>Tc mobility during long-term redox cycling. Our findings provide new constraints for modeling Tc fate at contaminated sites and in radioactive waste disposal.

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Publication Details

Journal
Environmental Science & Technology
Published
2025-12-14
DOI
https://doi.org/10.1021/acs.est.5c12024
Primary Topic
Radioactive element chemistry and processing
Type
article
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article

Technetium Retention and Remobilization Potential after Prolonged Reaction in Fe(III)- and Sulfate-Reducing Model Aquifer Systems

Samuel Shaw, Kathy Dardenne, Jonathan Richard Lloyd, Gareth T. W. Law et al.
Environmental Science & Technology
Radioactive element chemistry and processing
article

Technetium Retention and Remobilization Potential after Prolonged Reaction in Fe(III)- and Sulfate-Reducing Model Aquifer Systems

Samuel Shaw, Kathy Dardenne, Jonathan Richard Lloyd, Gareth T. W. Law, Gianni F. Vettese, Christopher Boothman, Katherine Morris, Carolyn I. Pearce, Mallory S. Ho
article en

Abstract

<sup>99</sup>Tc is a long-lived radioactive fission product whose subsurface mobility is governed by redox conditions. Under oxic conditions, soluble Tc(VII)O<sub>4</sub><sup>-</sup> is mobile, whereas under reducing conditions, poorly soluble Tc(IV) phases limit transport. Microcosm studies have frequently reported TcO<sub>2</sub>-like solids and, less consistently, Tc(IV)-sulfides. The stability of Tc(IV)-sulfides under environmentally relevant conditions remains unclear. Here, we used flowing sediment columns representative of the Sellafield subsurface to examine Tc speciation and stability over ∼1 year. Under reducing conditions, >90% of added TcO<sub>4</sub><sup>-</sup> (400 μg) was retained under both Fe(III)- and sulfate-reducing conditions. X-ray absorption spectroscopy showed TcO<sub>2</sub>-like phases dominated in Fe(III)-reducing columns, while Tc(IV)-sulfides dominated after sustained sulfate reduction. Sequential extractions indicated that Tc in sulfidic sediments was more recalcitrant (≤23% released by weak acids) than in Fe(III)-reducing systems (∼60% released). With oxic groundwater pumping, effluent Tc sourced from the sediments rose rapidly. Over 160 days, the sulfidic columns remobilized ∼25% of their Tc inventory compared to ∼50% in Fe(III)-reducing columns. The Tc(IV)-sulfides also gradually oxidized to form TcO<sub>2</sub> phases. While Tc(IV)-sulfides may enhance Tc retention under reducing conditions, TcO<sub>2</sub> phases more likely govern <sup>99</sup>Tc mobility during long-term redox cycling. Our findings provide new constraints for modeling Tc fate at contaminated sites and in radioactive waste disposal.

Environmental Science & TechnologyVol. 59(50)
Karlsruhe Institute of Technology (DE), University of Helsinki (FI), Pacific Northwest National Laboratory (US), University of Manchester (GB), Research Institute of Radio (RU)
Openalex Percentile: Top 66%
Radioactive element chemistry and processing
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