Japan Geoscience Union Meeting 2014

Presentation information

Oral

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

[M-IS21_28PM1] Biogeochemistry

Mon. Apr 28, 2014 2:15 PM - 4:00 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:Ichiro Tayasu(Center for Ecological Research, Kyoto University), Tomoya Iwata(Faculty of Life and Environmental Sciences, University of Yamanashi), Rota Wagai(National Institute for Agro-Environmental Sciences, Carbon & Nutrient Cycling Division), Kazuya Nishina(National Institute for Enviromental Studies)

3:15 PM - 3:30 PM

[MIS21-16] How does anthropogenic nitrogen input affect the nutrient dynamics and food web structures?

*Nobuhito OHTE1, Hiroyuki TOGASHI2, Naoko TOKUCHI3, Mayumi YOSHIMURA4, Yoshikazu KATO5, Naoto F. ISHIKAWA6, Michio KONDO7, Ichiro TAYASU5 (1.Graduate School of Agricultural and Life Sciences, University of Tokyo, 2.Field Science Education and Research Center, Kyoto University, 3.Tohoku National Fisheries Research Institute, Fisheries Research, 4.Japan Agency for Marine-Earth Science and Technology, 5.Faculty of Science and Technology, Ryukoku University, 6.Center for Ecological Research, Kyoto University, 7.Kansai Research Center, Forestry and Forest Products Research)

Keywords:river ecosystem, nitrogen input, stable isotope, food web

In last five decades, impacts of anthropogenic nutrient inputs on river ecosystems have continuously been a major concern for the governments and residents of the catchments in Japan. Major sources of anthropogenic nitrogen (N) include leachate from forest ecosystem, surplus fertilizers and sewage. Impacts of anthropogenic N inputs on nutrient dynamics and food web structures were investigated using stable N isotope techniques in the Arida river catchment, Japan. Riverine survey utilizing 5 regular sampling points showed that δ15N of nitrate (NO3-) increased from forested upstream (~2 ‰) to the downstream (~7 ‰) due to the sewage loads and fertilizer effluents from agricultural area. Correspondingly the δ15N of benthic algae and aquatic insects increased toward the downstream. This indicates that primary producers of each reach strongly relied on the local N sources and it was utilized effectively in their food web. Simulation using a GIS based mixing model considering the spatial distributions of human population density and fertilizer effluents revealed that strongest impacts of N inputs was originated from organic fertilizers applied to orchards in the middle to lower parts of catchment. Differences in δ15N between primary producers and predators were ~6-7 ‰ similarly at all sampling points. Food web structural analysis using food network unfolding technique based on observed δ15N suggested that the structure of nutrient pyramid did not differ significantly along the riverine positions, while the members of species in each trophic revel changed and the impact of anthropogenic N input was visible along the river.