4.6 Article

Nitrogen addition changes grassland soil organic matter decomposition

Journal

BIOGEOCHEMISTRY
Volume 125, Issue 2, Pages 203-219

Publisher

SPRINGER
DOI: 10.1007/s10533-015-0123-2

Keywords

Carbon; Fertilization; Microbial respiration; Soil aggregate; Nutrient Network; Wet sieving

Funding

  1. Cedar Creek Long Term Ecological Research Program [NSF DEB-1234162]
  2. National Science Foundation Graduate Research Fellowship [00039202]
  3. Dayton Fund of Bell Museum of Natural History
  4. National Science Foundation Research Coordination Network
  5. Long Term Ecological Research programs
  6. University of Minnesota's Institute on Environment
  7. Division Of Environmental Biology
  8. Direct For Biological Sciences [1234162] Funding Source: National Science Foundation

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Humans have dramatically increased the deposition and availability of nutrients, such as nitrogen (N), worldwide. Soil organic matter (SOM) is a significant global reservoir of carbon (C); however, the effects of N enrichment on this large, heterogeneous C stock are unclear. Nitrogen has variable effects on the biological, chemical, and physical factors that determine SOM pool mean residence time; consequently, we predicted that N enrichment would have distinct effects on SOM pools, including the pool that is readily available for microbial decomposition, as well as the pools that have been stabilized against microbial decomposition via aggregate occlusion and mineral association. We addressed this gap in knowledge by measuring the effects of N addition on different SOM pools at five grassland experiments in the US Central Great Plains that participate in the Nutrient Network and have been fertilized for three or five years. Overall, N addition decreased microbial respiration of unoccluded OM by as much as 29 % relative to control plots, and consequently, decreased C loss from this pool. Furthermore, N addition tended to increase soil aggregation and C occlusion in large macro-aggregates. These results suggest that N addition will increase C sequestration by slowing the decomposition of SOM, as well as stabilizing SOM against microbial decomposition in aggregate-occluded pools. However, the effects of N on all pools studied varied among sites, possibly due to site variation in soil texture. Consequently, increased sequestration of soil C in response to N enrichment may not be universal across grasslands.

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