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Dynamics of litter carbon turnover and microbial abundance in a rye detritusphere
Authors:Christian Poll  Sven Marhan  Joachim Ingwersen  Ellen Kandeler
Institution:1. Institute of Soil Science and Land Evaluation, Soil Biology Section, University of Hohenheim, Emil-Wolff-Straße 27, 70599 Stuttgart, Germany;2. Institute of Soil Science and Land Evaluation, Biogeophysics Section, University of Hohenheim, Emil-Wolff-Straße 27, 70599 Stuttgart, Germany;1. CSIRO Entomology, PMB No 2, Glen Osmond, SA 5064, Australia;2. School of Environment and Natural Resources, Ohio State University, Columbus, OH 43210, USA;3. Odum School of Ecology, Ecology Annex, University of Georgia, Athens, GA 30602-2360, USA
Abstract:Factors determining C turnover and microbial succession at the small scale are crucial for understanding C cycling in soils. We performed a microcosm experiment to study how soil moisture affects temporal patterns of C turnover in the detritusphere. Four treatments were applied to small soil cores with two different water contents (matric potential of ?0.0063 and ?0.0316 MPa) and with or without addition of 13C labelled rye residues (δ13C=299‰), which were placed on top. Microcosms were sampled after 3, 7, 14, 28, 56 and 84 days and soil cores were separated into layers with increasing distance to the litter. Gradients in soil organic carbon, dissolved organic carbon, extracellular enzyme activity and microbial biomass were detected over a distance of 3 mm from the litter layer. At the end of the incubation, 35.6% of litter C remained on the surface of soils at ?0.0063 MPa, whereas 41.7% remained on soils at ?0.0316 MPa. Most of the lost litter C was mineralised to CO2, with 47.9% and 43.4% at ?0.0063 and ?0.0316 MPa, respectively. In both treatments about 6% were detected as newly formed soil organic carbon. During the initial phase of litter decomposition, bacteria dominated the mineralisation of easily available litter substrates. After 14 days fungi depolymerised more complex litter compounds, thereby producing new soluble substrates, which diffused into the soil. This pattern of differential substrate usage was paralleled by a lag phase of 3 days and a subsequent increase in enzyme activities. Increased soil water content accelerated the transport of soluble substrates, which influenced the temporal patterns of microbial growth and activity. Our results underline the importance of considering the interaction of soil microorganisms and physical processes at the small scale for the understanding of C cycling in soils.
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