Organic carbon (OC) associated with reactive metal oxides, especially noncrystalline ferric iron [Fe(III)] and aluminum (Al) (hydr)oxides, is commonly assessed by the citrate-bicarbonate-dithionite (CBD) method (termed "metal-bound OC" or abbreviated as "OC CBD " hereafter) and estimated to constitute 15%-38% of total OC in sediments and upland soils (Shields et al., 2016;Zhao et al., 2016). However, the relative importance of OC CBD in different land types (e.g., uplands vs. wetlands) and soil depths remains unclear (Mu et al., 2016;Rasmussen et al., 2018;Wan et al., 2019;Zhao et al., 2016), hampering our ability to predict and protect this important OC pool that is vital for the long-term preservation of soil organic carbon (SOC) (Hemingway et al., 2019;Schmidt et al., 2011).While reactive Fe is assumed to play a central role in binding OC, its content has no relationship with the SOC-normalized concentration of OC CBD at regional scales (Mu et al., 2016;Zhao, et al., 2016). Recent evidence suggests that other polyvalent cations and/or mineral phases including manganese (Mn) and silicate (Si) may also be solublized during the CBD treatment and contribute to OC binding (Jugsujinda et al., 1995;Paterson et al., 1993). In particular, calcium (Ca), one of the most abundant polyvalent cations in soils (Rowley et al., 2018), can promote Fe-OC association by forming Fe-OC-Ca ternary co-precipitates (Adhika-