4.7 Article

Rhizosphere priming effects on soil carbon and nitrogen mineralization

Journal

SOIL BIOLOGY & BIOCHEMISTRY
Volume 76, Issue -, Pages 183-192

Publisher

PERGAMON-ELSEVIER SCIENCE LTD
DOI: 10.1016/j.soilbio.2014.04.033

Keywords

Rhizosphere priming effect; SOM decomposition; Gross nitrogen mineralization; Microbial biomass; Extracellular enzyme activity; Rhizosphere respiration

Categories

Funding

  1. National Research Initiative of the U.S. Department of Agriculture's Cooperative State Research, Education and Extension Service [2006-35107-17225]
  2. Division of Environmental Biology of the U.S. National Science Foundation [1354659]
  3. Direct For Biological Sciences [1354098] Funding Source: National Science Foundation
  4. Division Of Environmental Biology [1354098] Funding Source: National Science Foundation
  5. Division Of Environmental Biology
  6. Direct For Biological Sciences [1354659, 1354920] Funding Source: National Science Foundation

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Living roots and their rhizodeposits affect microbial activity and soil carbon (C) and nitrogen (N) mineralization. This so-called rhizosphere priming effect (RPE) has been increasingly recognized recently. However, the magnitude of the RPE and its driving mechanisms remain elusive. Here we investigated the RPE of two plant species (soybean and sunflower) grown in two soil types (a farm or a prairie soil) and sampled at two phenological stages (vegetative and mature stages) over an 88-day period in a greenhouse experiment. We measured soil C mineralization using a continuous C-13-labeling method, and quantified gross N mineralization with a N-15-pool dilution technique. We found that living roots significantly enhanced soil C mineralization, by 27-245%. This positive RPE on soil C mineralization did not vary between the two soils or the two phenological stages, but was significantly greater in sunflower compared to soybean. The magnitude of the RPE was positively correlated with rhizosphere respiration rate across all treatments, suggesting the variation of RPE among treatments was likely caused by variations in root activity and rhizodeposit quantity. Moreover, living roots stimulated gross N mineralization rate by 36-62% in five treatments, while they had no significant impact in the other three treatments. We also quantified soil microbial biomass and extracellular enzyme activity when plants were at the vegetative stage. Generally, living roots increased microbial biomass carbon by 0-28%, beta-glucosidase activity by 19-56%, and oxidative enzyme activity by 0-46%. These results are consistent with the positive rhizosphere effect on soil C (45-79%) and N (10-52%) mineralization measured at the same period. We also found significant positive relationships between beta-glucosidase activity and soil C mineralization rates and between oxidative enzyme activity and gross N mineralization rates across treatments. These relationships provide clear evidence for the microbial activation hypothesis of RPE. Our results demonstrate that root-soil-microbial interactions can stimulate soil C and N mineralization through rhizosphere effects. The relationships between the RPE and rhizosphere respiration rate and soil enzyme activity can be used for explicit representations of RPE in soil organic matter models. Published by Elsevier Ltd.

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