Phosphorus (P) is a macronutrient that limits plant growth in many ecosystems. Soils contain large amounts of organic P (OP) derived from plant detritus, which becomes available to plants through OP decomposition (see conceptual figure). Despite the fact that this process is crucial for plant nutrition, since plants can only take up inorganic P, the rate at which OP is decomposed and the time OP persists in soils before being decomposed remains poorly understood. Currently, many biogeochemical models are based on the assumption that the pools of soil OP and organic carbon turn over at the same rate. However, recent findings suggest that OP persists longer in soil than organic carbon that is not phosphorylated, because OP compounds sorb more rigidly to minerals than compounds without phosphate group, which likely decreases their decomposition rate.
At present, there are no reliable methods for determining the decomposition and turnover of OP in soils, which strongly hampers our ability to implement an accurate mechanistic representation of the P cycle in Earth system models. In contrast to carbon and nitrogen, P has only one stable isotope. In addition, the non-stable phosphorus isotopes have very short half-lives, which makes them unsuitable for exploring the long-term (i.e. >1 year) dynamics of phosphorus in terrestrial ecosystems. Thus, much less is known about the P cycle than about the carbon and nitrogen cycle in terrestrial ecosystems.
This project develops a new approach to study OP decomposition and turnover in soils. The project develops isotope methods to analyze the isotope signature of carbon in OP compounds, allowing us to determine their decomposition and turnover in soils. The results of this project open up new possibilities for studying P dynamics and make a fundamental advance in our understanding of the P cycle in terrestrial ecosystems. The goal of the project is to quantify the turnover time of different OP compounds and the total soil OP pool, understand the factors that determine the turnover, and reveal how soil OP turnover affects P cycling in terrestrial ecosystems.