Japan Geoscience Union Meeting 2014

Presentation information

Oral

Symbol M (Multidisciplinary and Interdisciplinary) » M-IS Intersection

[M-IS21_28PM2] Biogeochemistry

Mon. Apr 28, 2014 4:15 PM - 6:00 PM 511 (5F)

Convener:*Muneoki Yoh(Tokyo University of Agriculture and Technology), Hideaki Shibata(Field Science Center fot Northern Biosphere, Hokkaido University), Naohiko Ohkouchi(Japan Agency for Marine-Earth Science and Technology), Youhei Yamashita(Faculty of Environmental Earth Science, Hokkaido University), Chair:Rota Wagai(National Institute for Agro-Environmental Sciences, Carbon & Nutrient Cycling Division), Kazuya Nishina(National Institute for Enviromental Studies), Yoshiyuki Inagaki(Forestry and Forest Products Research Institute), Kazumichi Fujii(Forestry and Forest Products Research Institute)

5:15 PM - 5:30 PM

[MIS21-23] Soil nitrite transformation along a forest slope and controlling factors

*Megumi KUROIWA1, Kazuo ISOBE1, Hiroyu KATO1, Sho MURABAYASHI1, Yuka KANEKO1, Tomoki ODA1, Nobuhito OHTE1, Shigeto OTSUKA1, Keishi SENOO1 (1.Graduate School of Agricultural and Life Sciences, The University of Tokyo)

Keywords:Forest soil, Nitrite, 15N tracer, Dissolved organic nitrogen, Nitrification

We conducted a tracer study to clarify the spatial heterogeneity of nitrite (NO2-) dynamics in forest soils. Because of its reactive nature, NO2- does not usually accumulate in forest soils. This low concentration and experimental difficulties of accurate quantification have hampered quantitative detailed analyses of gross NO2- production and consumption in terrestrial environments. However, NO2- is an intermediate in many N transformation processes including nitrification and denitrification. Furthermore NO2- can also be reduced to gaseous N and react with organic matter not only biologically but also chemically. Thus NO2- dynamics may control whole N retention/emission characteristics in forest soils. We added 15NO2- to mineral top soils derived from a slope of a Japanese cedar forest. Primary properties of soils such as concentration of inorganic N, pH and water content differed geographically; N concentration, pH and water content are lower in the upper soils. NO2- production and consumption rates gradually increased from upper slope to lower slope. Quite short mean residence time of NO2- implies that NO2- consumed very rapidly anywhere in slope. The dominant pathway of NO2- consumption change geographically. It is suggested that the conversion to DON and gaseous N is more important in upper soils. On the other hand, conversion to NO3- (nitrification) is dominant in lower soils.At this presentation, we focus on geographical difference of NO2- dynamics and their regulation by environmental factors.