Daniel Olk1, David Laird1, and Michael Thompson2. (1) USDA-ARS National Soil Tilth Lab., 2150 Pammel Drive, Ames, IA 50011, (2) Iowa State University, Iowa State University, 2503 Agronomy Hall, Ames, IA 50011-1010
Some biomolecules
in soil organic matter (SOM) are intrinsically more resistant to microbial
decomposition than are other SOM components. Their resistance can be altered by
soil properties and by land management, which can affect the formation and
stability of soil organic matter and in turn soil processes. Selected
examples follow. First, black carbon in three Midwestern soils was found to be preferentially
concentrated in the coarse clay subfraction.
It consisted principally of aromatic C that might had originally been charcoal
formed during prairie fires and that had since attracted aliphatic biogenic
C. The black C had old radiocarbon ages
and was interpreted to be less bioavailable than more recent biogenic compounds.
Medium and fine clay subfractions
were dominated by modern biogenic C, which was dominantly aliphatic. Second, in a study of two Iowa soils, humic acid in the clay fraction
was enriched in readily oxidizable molecules compared to the humic acid in the silt
fraction. Humic acid in a poorly drained clayey soil had more aromatic C,
including charcoal–like moieties, while humic acid in a sandy, well drained
soil had more aliphatic compounds, readily combustible carbohydrates and
lignin. Third, lignin-derived phenolic compounds often accumulate in flooded soils,
apparently contributing simultaneously to both C sequestration and an impedance
of N cycling. Their accumulation is
affected by crop rotation and also soil aeration during crop residue
decomposition. In aerobic soils, phenols
have been associated with medium-term soil aggregation. Improved chromatographic
and spectroscopic analyses for phenols will better elucidate their origins and
their roles in C stabilization and nutrient cycling. Finally,
a few studies that characterized SOM chemistry following long-term animal
manure incorporation showed mainly an accumulation of fatty acids. These examples
reflect the interplay of soil properties and land management that affects the resistance
of biomolecules to microbial decomposition and their enrichment in soils.