Abstract. Pyrogenic organic matter (PyOM) is a major and persistent component of soil organic matter, but its
mobility and cycling in soils is largely unknown. We conducted a column experiment with a topsoil
and subsoil of a sand and a sandy loam to study the mobility of highly 13C labeled
ryegrass PyOM (>2.8 at. %), applied as a layer on a 7 cm long soil column, under
saturated conditions. Further, we used fresh and oxidized PyOM (accelerated aging with
H2O2) to identify changes in its migration through the soil with aging and associated
surface oxidation. Due to the isotopic signature, we were able to trace the PyOM carbon (PyOM-C)
in the soil columns, including density fractions, its effect on native soil organic carbon (nSOC)
and its total export in percolates sequentially sampled after 1000–18 000 L m−2. In
total, 4 %–11 % of the added PyOM-C was mobilized and <1 % leached from the
columns. The majority of PyOM-C was mobilized with the first flush of 1000 L m−2
(51 %–84 % of exported PyOM-C), but its export was ongoing for the sandy soil and the
loamy subsoil. Oxidized PyOM showed a 2–7 times higher mobility than fresh PyOM. In addition,
2-fold higher quantities of oxidized PyOM-C were leached from the sandy soil compared to the
loamy soil. Besides the higher mobility of oxidized PyOM, its retention in both soils increased
due to an increased reactivity of the oxidized PyOM surfaces and enhanced the interaction with the
soil mineral phase. Density fractionation of the upper 0–2.3 cm, below the PyOM
application layer, revealed that up to 40 % of the migrated PyOM was associated with the mineral
phase in the loamy soil, highlighting the importance of mineral interaction for the long-term fate
of PyOM in soils. The nSOC export from the sandy soil significantly increased by
48 %–270 % with addition of PyOM compared to the control, while no effect was found for
the loamy soil after the whole percolation. Due to its high sorption affinity towards the soil
mineral phase, PyOM can mobilize mineral-associated soil organic matter in coarse-textured soils,
where organo-mineral interactions are limited, while finer-textured soils have the ability to
re-adsorb the mobilized soil organic matter. Our results show that the vertical mobility of PyOM
in soils is limited to a small fraction. Aging (oxidation) increases this fraction but also
increases the PyOM surface reactivity and thus its long-term retention in soils. Moreover, the
migration of PyOM affects the cycling of nSOC in coarse soils and thus influences the carbon cycle
of fire-affected soils.