Input of easily available organic C and N stimulates microbial decomposition of soil organic matter in arctic permafrost soil
0301 basic medicine
VDP::Landbruks- og fiskerifag: 900::Landbruksfag: 910::Landbruksteknologi: 916
570
Organic matter decomposition
Dewey Decimal Classification::500 | Naturwissenschaften::570 | Biowissenschaften, Biologie
Nitrogen
Microorganisms
Soil Science
Permafrost
Microbial decomposition
Microbiology
630
ALLOCATION
Article
CARBON
Microbial community composition
03 medical and health sciences
NITROGEN DYNAMICS
Organic compounds
SDG 13 - Climate Action
Climate change
MINERALIZATION
Cellulose
TEMPERATURE
Tundra
BEECH FOREST SOIL
Phospholipids
Decomposer communities
VDP::Agriculture and fisheries science: 900::Agricultural sciences: 910::Agricultural technology: 916
FUNGAL
2. Zero hunger
106022 Mikrobiologie
LIMITATION
:Agriculture and fisheries science: 900::Agricultural sciences: 910::Agricultural technology: 916 [VDP]
Phospholipid fatty acid (PLFA)
Proteins
Biogeochemistry
Extracellular enzymes
15. Life on land
:Landbruks- og fiskerifag: 900::Landbruksfag: 910::Landbruksteknologi: 916 [VDP]
TUNDRA
Glucose
Priming
13. Climate action
SDG 13 – Maßnahmen zum Klimaschutz
106022 Microbiology
Amino acids
COMMUNITIES
DOI:
10.1016/j.soilbio.2014.04.014
Publication Date:
2014-04-22T08:01:31Z
AUTHORS (18)
ABSTRACT
Rising temperatures in the Arctic can affect soil organic matter (SOM) decomposition directly and indirectly, by increasing plant primary production and thus the allocation of plant-derived organic compounds into the soil. Such compounds, for example root exudates or decaying fine roots, are easily available for microorganisms, and can alter the decomposition of older SOM ("priming effect"). We here report on a SOM priming experiment in the active layer of a permafrost soil from the central Siberian Arctic, comparing responses of organic topsoil, mineral subsoil, and cryoturbated subsoil material (i.e., poorly decomposed topsoil material subducted into the subsoil by freeze-thaw processes) to additions of 13C-labeled glucose, cellulose, a mixture of amino acids, and protein (added at levels corresponding to approximately 1% of soil organic carbon). SOM decomposition in the topsoil was barely affected by higher availability of organic compounds, whereas SOM decomposition in both subsoil horizons responded strongly. In the mineral subsoil, SOM decomposition increased by a factor of two to three after any substrate addition (glucose, cellulose, amino acids, protein), suggesting that the microbial decomposer community was limited in energy to break down more complex components of SOM. In the cryoturbated horizon, SOM decomposition increased by a factor of two after addition of amino acids or protein, but was not significantly affected by glucose or cellulose, indicating nitrogen rather than energy limitation. Since the stimulation of SOM decomposition in cryoturbated material was not connected to microbial growth or to a change in microbial community composition, the additional nitrogen was likely invested in the production of extracellular enzymes required for SOM decomposition. Our findings provide a first mechanistic understanding of priming in permafrost soils and suggest that an increase in the availability of organic carbon or nitrogen, e.g., by increased plant productivity, can change the decomposition of SOM stored in deeper layers of permafrost soils, with possible repercussions on the global climate.
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