Soils represent the largest terrestrial carbon pool, a majority of which come from atmospheric CO 2 that is fixed through photosynthesis by the terrestrial biosphere (Stockmann et al., 2013). The exchange of carbon between the atmosphere and the terrestrial biosphere makes soils an archive of past environmental changes (Pachauri et al., 2014). For example, the stable carbon isotopic composition (δ 13 C) of soil organic matter (SOM) has been used to approximate the δ 13 C of CO 2 produced by soil respiration-a key parameter in using paleosols to reconstruct paleoatmospheric CO 2 levels (Breecker, 2010;Cerling, 1992). Moreover, the δ 13 C SOM of ancient soils, or paleosols, have been widely used to narrate the evolution history of aboveground vegetation habitat as well as hominin environments (e.g., Cerling, 1991;Ehleringer et al., 1997).The decomposition of SOM represents a significant obstacle when using δ 13 C SOM records to reconstruct paleoenvironments (Bowen & Beerling, 2004). SOM is a mixture of organic compounds (e.g., lipids, lignins) of both plant and microbial origins, featuring distinct δ 13 C signals, physicochemical properties, and reaction kinetics (Ehleringer et al., 2000). Changes in the relative abundances of those compounds during SOM degradation could cause 13 C fractionation, altering the δ 13 C signal of fresh, undegraded soils. In well-drained, modern soil profiles, the decrease of total organic carbon content (TOC) along depth usually occurs concomitantly with a progressive increase of δ 13