B18-Core EXAFS
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Diamond Proposal Number(s):
[30629]
Abstract: Geopolymer cements are highly promising materials for long-term immobilisation of Strontium-90 radioactive waste, offering superior durability and cation binding sites compared to conventional Portland cement matrices. This study investigates the influence of prolonged leaching on the Sr immobilisation mechanism and structural integrity of metakaolin-based geopolymers using the ANSI/ANS 16.1 semi-dynamic leaching test. All geopolymers demonstrated high Sr retention, with Leachability Indices at least 14.7 for all samples, significantly exceeding the industry guideline of 6.0, confirming their effectiveness. Importantly, potassium silicate–activated geopolymers exhibited reduced Sr release and substantially lower leaching rates than sodium silicate–activated geopolymers. Multiscale spectroscopic and diffractometric analysis, including synchrotron X-ray absorption spectroscopy and multinuclear high-field solid-state MAS NMR probing 39K, 23Na, 27Al, and 29Si, revealed that the alkali aluminosilicate gel framework remained structurally stable after leaching for 28 days, with no significant alterations to Si and Al bonding environments. Sr release is primarily controlled by diffusion, and the dominant immobilisation mechanism is the formation of insoluble SrCO3. Atomic-level Sr structural analysis using XANES/EXAFS revealed an increase in the average Sr coordination number in both systems after leaching, with a more pronounced rise in potassium-based geopolymers, consistent with enhanced SrCO3 formation. Overall, these findings demonstrate that geopolymers maintain structural integrity during leaching and show for the first time that using potassium rather than sodium as an alkali activator is definitively more advantageous for maximising the long-term effectiveness of geopolymer wasteforms. This demonstrates their strong suitability as wasteforms for the safe long-term immobilisation of Sr-containing radioactive wastes.
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Jul 2026
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B18-Core EXAFS
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Diamond Proposal Number(s):
[37458]
Open Access
Abstract: Geopolymers are a promising alternative to conventional Portland cement-based wasteforms for immobilising hazardous radioactive fission products such as caesium-137 and strontium-90, offering superior durability and lower leach rates. However, the specific mass transport mechanisms governing radionuclide release in geopolymers remain poorly understood, limiting implementation. This study reveals the incorporation and mass transport mechanisms of caesium and strontium in metakaolin-based geopolymers. Solid-state characterisation showed Sr incorporation via direct chemical binding in the chemical binding in the alkali aluminosilicate hydrate gel in chargebalancing extra-framework sites, replacing K + ions, and precipitation of SrCO 3 and Sr(OH) 2 , while Cs is predominantly bound within the charge-balancing sites in the alkali aluminosilicate gel. Leach testing confirmed low overall release rates, with all measured Leachability Indices significantly exceeding the industry minimum of 6 (Li > 13 for Cs; Li > 18 for Sr), outperforming conventional PC systems. Mass transport modelling revealed distinct mechanisms: Cs release is accurately described by a Diffusion/Surface Exchange Kinetics Model (DSEM), yielding high correlation (R 2 > 0.99). However, Sr exhibited a complex, staggered release profile. Standard mass transport models (diffusion, dissolution, surface exchange) could not satisfactorily capture this complex behaviour. We hypothesise this rate resumption is caused by the structural reordering or crystallisation of the amorphous K-A-S-H gel into a zeolitic phase, potentially excluding incorporated Sr. This finding highlights that simple diffusive models, commonly assumed for geopolymers, are inadequate for predicting the long-term per-1 formance of Sr-containing geopolymer wasteforms. The new insight presented here is critical development of geopolymers for radioactive waste disposal.
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Jan 2026
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B18-Core EXAFS
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Diamond Proposal Number(s):
[31395, 37736]
Abstract: Selenium-79, a radionuclide present in higher-activity radioactive wastes destined for deep geological disposal, is mobile under oxic conditions, where Se(IV) and Se(VI) dominate. Anoxic batch microcosm incubations were constructed containing Wyoming MX80 bentonite (a candidate buffer material in geological disposal) and artificial groundwater with or without steel coupons to represent canister materials. Se(VI)(aq) bioreduced and was removed by 7 days when lactate was added as an electron donor, after which sulfate reduction occurred. With H2 gas as the electron donor, Se(VI) bioreduction slowed, with complete removal at 14 days and minimal sulfate reduction thereafter. 16S rRNA gene sequencing highlighted the dominance of Anaerobacillus spp. (44% at 28 days) during Se(VI)-reduction, and in the lactate-amended systems, there was a subsequent enrichment in sulfate-reducing bacteria affiliated with Desulfosporosinus spp. (60% relative abundance at 84 days). Extended X-ray absorption fine structure (EXAFS) analyses identified monoclinic Se(0) as the bioreduction product after 28 days, but by 84 days this evolved to trigonal Se(0) in the absence of steel coupons or was further reduced to FeSe2 with steel present. The reduction of Se(VI)(aq) to poorly soluble Se(0)/FeSe2 mediated by indigenous bentonite microbial communities highlights their potential importance in promoting Se-79 retention during deep geological disposal.
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Jan 2026
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B18-Core EXAFS
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Diamond Proposal Number(s):
[37736]
Open Access
Abstract: 99Tc is a long-lived radioactive fission product whose subsurface mobility is governed by redox conditions. Under oxic conditions, soluble Tc(VII)O4– is mobile, whereas under reducing conditions, poorly soluble Tc(IV) phases limit transport. Microcosm studies have frequently reported TcO2-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 TcO4– (400 μg) was retained under both Fe(III)- and sulfate-reducing conditions. X-ray absorption spectroscopy showed TcO2-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 TcO2 phases. While Tc(IV)-sulfides may enhance Tc retention under reducing conditions, TcO2 phases more likely govern 99Tc 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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Dec 2025
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I19-Small Molecule Single Crystal Diffraction
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Thien D.
Duong
,
Jiangnan
Li
,
Ruohan
Li
,
Xin
Lian
,
Yinlin
Chen
,
Jiarui
Fan
,
Joseph
Hurd
,
Lixia
Guo
,
Daniel
Lee
,
Mark
Warren
,
Sihai
Yang
Diamond Proposal Number(s):
[41123]
Abstract: The capture of xenon (Xe) and krypton (Kr) from the off-gas of used nuclear fuel is of great importance to the treatment of radioactive wastes and production of high purity Xe. Solid sorbents, in particular metal–organic frameworks (MOFs), show promise in gas capture. However, the unknown radiation resistance of MOFs has limited their development. Herein, the efficient capture and separation of Xe/Kr by MFM-520, which strikes a remarkable stability toward 1750 kilogray (kGy) γ-irradiation, is reported. Under ambient conditions, dynamic breakthrough experiments confirm the efficient separation performance, yielding a Xe capacity of 66 and 0.2 mg g−1 from a by-product of air separation (Xe/Kr: 20/80; v/v) and off-gas (Xe/Kr: 400/40 ppm balance in air), respectively. In situ synchrotron X-ray single crystal diffraction and solid-state nuclear magnetic resonance (ssNMR) studies reveal that the optimal micropore of MFM-520 underpins specific host-guest interactions to Xe, resulting in selective Xe capture.
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Oct 2025
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B18-Core EXAFS
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Diamond Proposal Number(s):
[37736]
Abstract: There is a requirement to further understand the structural and thermal properties of candidate Pu wasteform materials, and moreover gain a better understanding of composition-driven variation in these properties as they can impact disposability. Zirconolite (CaZrTi2O7) phases are a candidate wasteform system to immobilise Pu at scale and therefore it is necessary to understand (as far as possible) the isolated influence of cation substitution on specific lattice sites. CaZr1-xHfxTi2O7 is a model system for understanding the microstructural effects of Hf4+ substitution and underpin its viability as a neutron absorbing additive that could feasibly be co-immobilised with Pu. Hf4+ was capable of wholly substituting for Zr4+ at low-to-moderate concentration (i.e. x ≤ 0.60) after which some minor Hf-phase segregation was observed. Powder X-ray diffraction, Rietveld analysis and Raman spectroscopy were consistent with Hf4+ substituting in the Zr4+ site and confirmed no additional zirconolite polytypes were formed in addition to 2M. Hf L3-edge EXAFS analysis was consistent with Hf4+ occupying the 7-fold Zr4+ site in the zirconolite-2M structure consistent with the targeted substitution scheme. The thermal diffusivity and thermal conductivity of the zirconolite ceramics was generally observed to increase with elevated Hf4+ content although no clear compositional trends were identified.
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Aug 2025
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I12-JEEP: Joint Engineering, Environmental and Processing
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Abstract: Waterside corrosion of zirconium (Zr) alloy nuclear fuel cladding occurs during normal operating conditions in pressurized water reactors. This corrosion yields zirconium oxide (ZrO2) and hydrogen, with a fraction of the hydrogen absorbed into the fuel cladding where it can redistribute through solid-state diffusion via concentration, temperature, and stress gradients. If the local hydrogen solubility in the metal is exceeded, then zirconium hydrides (ZrHx) precipitate in the zirconium matrix. Zirconium hydrides negatively impact the integrity of zirconium-based nuclear fuel cladding during both normal operation and extended dry storage through cladding embrittlement. With the desire to operate reactors with higher fuel enrichment and to higher fuel burnups, which will result in additional corrosion to the zirconium alloys, modeling hydrogen and hydride behavior is fundamental to ensuring safe reactor operations. Thus, this study aims to understand how applied tensile stress and irradiation-induced defects influence hydride precipitation and dissolution in zirconium alloys. In-situ synchrotron X-ray diffraction experiments were performed to study these influences in Zircaloy-4 under different thermo-mechanical conditions and levels of irradiation fluence. Additional analysis of Zircaloy-4 coupons under applied stress was also performed to explore the effect of stress on hydrogen migration and hydride dissolution. The applied tensile stress studies indicate that stress does not influence the dissolution solvus or the temperature hydrides completely dissolved at. Furthermore, the studies suggest that hydride nucleation is not noticeably changed by an applied tensile stress. However, hydride precipitation, defined by the Terminal Solid Solubility for Precipitation (TSSp), appears to slow under applied tensile stresses greater than or equal to 180 MPa. Furthermore, previous isothermal hydride growth experimental results were replicated and expanded on. Previous results were confirmed and indicate that applied tensile stresses slow hydride growth when the applied tensile stress is above the hydride reorientation threshold stress. Isothermal hydride growth did not result in the concentration of hydrogen in solid solution (Css) reaching the Terminal Solid Solubility for Dissolution (TSSd) during an isothermal hold, potentially reaching a quasi-equilibrium. It is hypothesized that the applied tensile stress impacts hydride growth rather than hydride nucleation. A potential explanation is that hydrides precipitating in different orientations due to the applied tensile stress have differences in hydride structure and dislocation networks. Studies on the influence of irradiation-induced defects on hydride precipitation and dissolution in as-irradiated and post-annealed materials were performed. Annealing the samples removed <a>-dislocations per the reduction in Full-Width at Half-Maximums (FWHMs) for alpha-Zr diffraction peaks. However, the FWHM of the alpha-Zr (002) peak did not change during the anneal, indicating that <c>-dislocation loops are still present and may still act as hydrogen traps. The delta (111) hydride diffraction peak integrated area was measured and found to increase from the as-irradiated to post-annealed state. This indicates hydrogen trapped by irradiation-induced defects in the material was released into solid solution and is available to form hydrides. The amount of hydrogen trapped by irradiation-induced defects was estimated at 12--63 wppm (8--47% of the total hydrogen content), which agrees with values reported in literature. TSSp and TSSd equations were fit to the data in both material states. Compared to the post-annealed data and literature, the as-irradiated TSSp and TSSd were lower. This is the opposite trend reported in literature for as-irradiated data. Little hydride growth during isothermal holds was observed in both the as-irradiated and post-annealed states.
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Jun 2025
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I14-Hard X-ray Nanoprobe
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F.
Dal Molin
,
D.
Hunt
,
A.
Dewar
,
S.
Lozach
,
C.
Phillips
,
B.
Thomas
,
L.
Warford
,
J. E.
Parker
,
J.
Walker
,
M.
Chocholek
,
D. M.
Paterson
,
H.
Woodward-Rowe
,
N.
Hicks
Diamond Proposal Number(s):
[35954]
Open Access
Abstract: Although oil and gas (O&G) derived produced waters and drill cuttings are known to contain enhanced levels of naturally occurring radium-228 (228Ra) and radium-226 (226Ra), most relevant ecological impact assessments have excluded radiological hazards and focus on other important contaminants, such as hydrocarbons and metals. Also, due to restricted access to the delimiting safety zone around operational O&G platforms, the few previous radioecological risk assessment studies have been conducted using seawater samples collected far from the main discharge point and applying default dilution and transfer factors to estimate concentrations of contaminants in biota. In this case study, sediment cores were collected close to a former O&G platform, Northwest Hutton (NWH), that used to be in the UK North Sea (61.11N, 1.31E). The sediment materials were analysed by gamma spectrometry and ICP-MS to confirm the presence of particles enriched in natural radioactivity. Benthic macrofaunal assemblages in the surrounding seabed were also characterised and one of the dominant species was selected for additional nano-hard X-Ray Fluorescence (nano-XRF) imaging to confirm the exposure pathways and refine the radioecological risk assessment using the ERICA tool. This novel approach for estimating dose rates was found to be less conservative than more traditional approaches using the ERICA default concentration ratio for 228Ra and 226Ra. The dose rate estimations were confirmed to be significantly lower than the ERICA screening level of 10μGy/h, in agreement with findings from previous studies.
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Mar 2025
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B18-Core EXAFS
I20-Scanning-X-ray spectroscopy (XAS/XES)
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Thomas S.
Neill
,
Katherine
Morris
,
Scott
Harrison
,
Pete
Apps
,
Nick
Bryan
,
Stephen
Parry
,
J. Frederick W.
Mosselmans
,
Giannantonio
Cibin
,
Bruce
Rigby
,
Francis R.
Livens
,
Samuel
Shaw
Diamond Proposal Number(s):
[17243, 21441]
Open Access
Abstract: Colloids present a challenge for nuclear decommissioning and disposal due to their potential to mobilise radionuclides. Waste retrieval and decommissioning of storage ponds for spent nuclear fuel and silos for radioactive waste at the Sellafield nuclear facility, UK, are high priorities. The particulates characterised here originate from facilities >60 years old and provide a unique opportunity to investigate the long-term fate of radionuclides in an aquatic, engineered storage environment. Radioactive effluents were obtained from a legacy pond and characterised using ultrafiltration, transmission electron microscopy (TEM) and actinide L3 edge X-ray absorption spectroscopy (XAS). TEM analysis showed discrete UO2-like nanoparticles, 5-10 nm in size, often co-associated with Mg-Al- and Fe-(oxyhydr)oxide colloidal phases. Uranium XAS indicated a mix of uranium oxidation states with EXAFS suggesting U(IV)-oxide nanoparticles and sorbed U(VI). Pu XANES identified Pu(IV) as the dominant oxidation state. Both U and Pu associates with large, Mg/Al- and Fe-(oxyhydr)oxide agglomerates highlights the potential for pseudo-colloid formation, explaining the basis of current particle filtration / abatement of technology. This study, which examines novel samples from a complex, highly radioactive facility using advanced techniques, provides a new understanding of radionuclide speciation and mobility in these environments and informs radioactive effluent treatment and disposal.
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Feb 2025
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B18-Core EXAFS
I20-Scanning-X-ray spectroscopy (XAS/XES)
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Diamond Proposal Number(s):
[24074, 21441]
Open Access
Abstract: Operations at uranium (U)-mining and nuclear facilities have left a global legacy of significant radionuclide contamination in groundwaters which must be managed to minimize environmental harm. Uranium groundwater contamination is present at several sites globally, including Oak Ridge National Laboratory and Hanford, USA and Sellafield nuclear site, UK. In situ phosphate biomineralisation offers a promising method for radionuclide (including 90Sr and U) remediation at these sites. Typically, phosphate-generating amendments are injected into the subsurface to sequester select radionuclides in groundwaters by precipitation of poorly soluble Ca-phosphate phases and subsequent adsorption and/or incorporation of radionuclides to these poorly soluble phases, a remediation route being explored for both U and 90Sr. In this study, we investigate the mechanisms of U-phosphate precipitation in two phosphate-generating amendments (Ca-citrate/Na-phosphate and glycerol phosphate) under conditions relevant to Sellafield, UK. Using aerobic batch sediment experiments, we show both Ca-citrate/Na-phosphate and glycerol phosphate amendments are effective at enhancing removal of U(VI) from representative groundwaters (from 94% to >97%). Aqueous geochemical data coupled to speciation modelling highlighted that precipitation of U(VI) phosphate phases was the likely mechanism of U(VI) removal from groundwaters. Further X-ray absorption spectroscopy (XAS) analysis of solids confirmed U was present as a highly insoluble uranyl orthophosphate-like phase after treatment with both Ca-citrate/Na-phosphate and glycerol phosphate amendments. These data provide underpinning information on U-phosphate remediation in Sellafield relevant conditions thus expanding the range of treatment options for radionuclide contaminated groundwaters and defining the transport and fate of U during phosphate biomineralisation.
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Feb 2025
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