4.6 Article

Impact of snowpack decrease on net nitrogen mineralization and nitrification in forest soil of northern Japan

Journal

BIOGEOCHEMISTRY
Volume 116, Issue 1-3, Pages 69-82

Publisher

SPRINGER
DOI: 10.1007/s10533-013-9882-9

Keywords

Freeze-thaw cycle; Nitrogen cycle; Resin core incubation; Experimental manipulation; Soil microbe; Nitrogen leaching

Funding

  1. Japan Society for the Promotion of Science [22248016, 25252026]
  2. Ministry of the Environment, Japan [S-9-3]
  3. Grants-in-Aid for Scientific Research [25252026, 22248016] Funding Source: KAKEN

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Winter climate change is an important environmental driver that alters the biogeochemical processes of forest soils. The decrease in snowpack amplifies soil freeze-thaw cycles and decreases the snowmelt water supply to soil. This study examined how snow decrease affects nitrogen (N) mineralization and nitrification in forest soil in northern Japan by conducting an in situ experimental snowpack manipulation experiment and a laboratory incubation of soil with different moisture, temperature and freeze-thaw magnitudes. For the incubation studies, surface mineral soil (0-10 cm) was collected from a cool-temperate natural mixed forest and incubated using the resin core method during the winter. In the field, there were two treatments: 50 and 100 % snow removal and control plots. The increase in the soil freeze-thaw cycle increased net N mineralization and marginally decreased the net nitrification in soil. The dissolved organic carbon (DOC) and DOC/DON ratio in soil increased with the decrease in snowpack especially during the snow melt period. These results suggested that the change in substrate quality by the increase in freeze-thaw cycles caused the significant enhancement of microbial ammonium production in soil. The lower soil moisture and higher gross immobilization of inorganic N by soil microbes may be maintaining the slow net nitrification and low nitrate leaching in freeze-thaw cycles with less snowpack. The results indicate that winter climate change would strongly impact N biogeochemistry through the increase in ammonium availability in soil for plants and microbes, whereas it would be unlikely that nitrate loss from surface soil would be enhanced.

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