Effect of accelerated carbonation on a Molybdenum-contaminated soil stabilized with magnesium oxide and limestone calcined clay cement

• Accelerated carbonation of stabilized soil with mixtures of MgO and LC3 up to 28 days. • Brucite carbonation leads to hydrated magnesium carbonates and potentially M-S-H • High Mo retention (>90%) maintained in MgO-containing treatments • Possible shift in main Mo retention minerals from brucite to HMCs and/or M-S-H A combination of magnesium oxide (MgO) and Limestone Calcined Clay Cement (LC3) has been previously identified as effective for the stabilization/solidification (S/S) of molybdenum (Mo) in a limestone tunnel sludge (Grand Paris express subway extension). However, the long-term performance of this S/S method is uncertain due to brucite's susceptibility to carbonation, the primary Mo-retaining phase. This study investigates the impact of accelerated carbonation on mineralogical transformations and Mo leaching behavior under controlled conditions (3% CO₂, 90% RH, 38°C) for up to 28 days. Mineralogical changes were monitored via XRD, TGA, and geochemical modeling. Leaching behavior was assessed using EN 12457-2 and US EPA 1313. Results show rapid carbonation of cementitious phases into calcite, with pH dropping from >12 to ≤10 within 6h, followed by brucite gradual reaction into poorly crystallized hydrated magnesium carbonates (HMCs) and potentially magnesium silicate hydrates (M-S-H). Mo leaching behavior was dependent on MgO content. In the formulations with 5 wt.% MgO, molybdenum release increased gradually but remained within acceptable limits, with retention attributed to uncarbonated brucite. In the 1 wt.% MgO + 3 wt.% LC3 formulation, Mo release initially spiked but stabilized at 0.03 mg/L after 28 days of carbonation, achieving over 90% leaching reduction and improved retention across a broader pH range (7-12). The durability of retention despite brucite carbonation suggests a shift in retention mechanisms from brucite sorption to possible immobilization by HMCs and/or M-S-H. Stabilized soils with MgO-LC3 mixture prove upon their efficacy in long-term Mo immobilization despite exposure to atmospheric CO 2 .

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Publication Details

Journal
Journal of Hazardous Materials Advances
Published
2026-04-23
DOI
https://doi.org/10.1016/j.hazadv.2026.101188
Primary Topic
Concrete and Cement Materials Research
Type
article
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article

Effect of accelerated carbonation on a Molybdenum-contaminated soil stabilized with magnesium oxide and limestone calcined clay cement

Ivan Serclerat, David S. Kosson, Bruno Huet, Nouffou Tapsoba et al.
Journal of Hazardous Materials Advances
Concrete and Cement Materials Research
article

Effect of accelerated carbonation on a Molybdenum-contaminated soil stabilized with magnesium oxide and limestone calcined clay cement

Ivan Serclerat, David S. Kosson, Bruno Huet, Nouffou Tapsoba, Amandine Dumas, Laurent de Windt, Florence Sanchez
article en

Abstract

• Accelerated carbonation of stabilized soil with mixtures of MgO and LC3 up to 28 days. • Brucite carbonation leads to hydrated magnesium carbonates and potentially M-S-H • High Mo retention (>90%) maintained in MgO-containing treatments • Possible shift in main Mo retention minerals from brucite to HMCs and/or M-S-H A combination of magnesium oxide (MgO) and Limestone Calcined Clay Cement (LC3) has been previously identified as effective for the stabilization/solidification (S/S) of molybdenum (Mo) in a limestone tunnel sludge (Grand Paris express subway extension). However, the long-term performance of this S/S method is uncertain due to brucite's susceptibility to carbonation, the primary Mo-retaining phase. This study investigates the impact of accelerated carbonation on mineralogical transformations and Mo leaching behavior under controlled conditions (3% CO₂, 90% RH, 38°C) for up to 28 days. Mineralogical changes were monitored via XRD, TGA, and geochemical modeling. Leaching behavior was assessed using EN 12457-2 and US EPA 1313. Results show rapid carbonation of cementitious phases into calcite, with pH dropping from >12 to ≤10 within 6h, followed by brucite gradual reaction into poorly crystallized hydrated magnesium carbonates (HMCs) and potentially magnesium silicate hydrates (M-S-H). Mo leaching behavior was dependent on MgO content. In the formulations with 5 wt.% MgO, molybdenum release increased gradually but remained within acceptable limits, with retention attributed to uncarbonated brucite. In the 1 wt.% MgO + 3 wt.% LC3 formulation, Mo release initially spiked but stabilized at 0.03 mg/L after 28 days of carbonation, achieving over 90% leaching reduction and improved retention across a broader pH range (7-12). The durability of retention despite brucite carbonation suggests a shift in retention mechanisms from brucite sorption to possible immobilization by HMCs and/or M-S-H. Stabilized soils with MgO-LC3 mixture prove upon their efficacy in long-term Mo immobilization despite exposure to atmospheric CO 2 .

Journal of Hazardous Materials AdvancesVol. 22
Vanderbilt University (US), Université Paris Sciences et Lettres (FR), Centre de Géosciences (FR), L3 Médical (France) (FR)
Life in Land
Openalex Percentile: Top 20%
Concrete and Cement Materials Research
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