Summary Isotopic fractionation of dissolved organic carbon percolating through the soil is often interpreted as due to microbial transformation. We investigated the potential effects of sorption on the δ 13 C of dissolved organic C in field and laboratory experiments. We sampled the organic C in soil water at two forested sites and measured sorption with intact mineral soil and individual minerals (dolomite, ferrihydrite, goethite, and quartz). The dissolved organic C was separated into hydrophilic and hydrophobic fractions using a resin approach. The δ 13 C values of bulk soils, alkaline‐extractable organic C, and dissolved organic C and its fractions were measured. Hydrophilic and hydrophobic fractions in forest floor seepage water were characterized by 13 C‐NMR spectroscopy. At both sites, δ 13 C of dissolved organic C increased with increasing depth, suggesting that decomposition contributes to the loss of the dissolved organic C. However, there was an enrichment of hydrophilic organic C in the soil solution as the water moved down the soil. The δ 13 C values of hydrophilic fractions were less negative than those of hydrophobic fractions. The smaller δ 13 C in the hydrophobic fraction was due to the large contribution of compounds derived from lignin that are depleted in 13 C. As the isotope composition of both fractions of dissolved organic C did not change throughout the profile, changes in δ 13 C of total organic C reflected changes in the relative proportions of its hydrophilic and hydrophobic fractions. The sorption experiments with minerals and soil cores gave similar results. When dissolved organic C came into contact with mineral material, the δ 13 C of that remaining in solution increased due to preferential sorption of the 13 C‐depleted hydrophobic fractions. Moreover, the soils released hydrophilic organic C with large δ 13 C values, increasing the δ 13 C of organic C in effluents from soil compared with that in the inflow. Thus, selective sorption of organic C fractions changes δ 13 C in a way that mimics metabolic transformation and decomposition.
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Kaiser et al. (2001) studied this question.
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