COS 55-10
δ15N of soil available N along a 3200 km long transect in Northern China

Wednesday, August 13, 2014: 11:10 AM
302/303, Sacramento Convention Center
Yunting Fang, State Key Laboratory of Forest and Soil Ecology, Instituted of Applied Ecology, Chinese Academy of Sciences, Shenyang, China
Dongwei Liu, State Key Laboratory of Forest and Soil Ecology, Instituted of Applied Ecology, Chinese Academy of Sciences, Shenyang, China
Weixing Zhu, Biological Sciences, State University of New York - Binghamton, Binghamton, NY
Ying Tu, State Key Laboratory of Forest and Soil Ecology, Instituted of Applied Ecology, Chinese Academy of Sciences, Shenyang, China
Chao Wang, State Key Laboratory of Forest and Soil Ecology, Instituted of Applied Ecology, Chinese Academy of Sciences, Shenyang, China
Edith Bai, State Key Laboratory of Forest and Soil Ecology, Instituted of Applied Ecology, Chinese Academy of Sciences, Shenyang, China
Haiyan Ren, State Key Laboratory of Forest and Soil Ecology, Instituted of Applied Ecology, Chinese Academy of Sciences, Shenyang, China
Chao Wang, State Key Laboratory of Forest and Soil Ecology, Instituted of Applied Ecology, Chinese Academy of Sciences, Shenyang, China
Xingguo Han, State Key Laboratory of Forest and Soil Ecology, Instituted of Applied Ecology, Chinese Academy of Sciences, Shenyang, China
Background/Question/Methods

Nitrogen (N) isotope is widely considered as an integrator of N cycling in terrestrial ecosystems, and has the potential to reveal spatial and temporal patterns of N cycling and predict the response of N cycles to natural and human disturbances. At the global scale, a pattern of decreased δ15N of soil and plant leaf with increasing mean annual precipitation (MAP) has been demonstrated for more two decades. However, the mechanisms causing this pattern are not clear. One possibility is that N losses relative to pool sizes are greater at drier sites and, because N lost (volatilization, denitrification and leaching) is typically depleted in 15N, leading to 15N-enrichment of soil and plants. Accordingly, we expect that δ15N of both ammonium and nitrate will decline with increasing precipitation. To test this hypothesis, we explored a regional pattern of 15N natural abundance for plant leaves, bulk soil as well as soil nitrate and ammonium along a 3200-km grassland transect in northern China. Soil samples were obtained from 36 sites, extending from Xinjiang Province at West to Inner Mongolian at East. The entire transect covered a MAP gradient from 30 to 500 mm.

Results/Conclusions

Soil ammonium concentration decreased and then increased along the MAP gradient, with a breakpoint at MAP around 200 mm. However, the δ15N of ammonium decreased monotonically with increasing precipitation. High and positive δ15N values in the arid region suggested a strong ammonia volatilization, associated with high pH values (on average 8.2). Nitrate concentration displayed no clear trend when MAP > 100 mm. Extremely high concentration (> 100 mg N kg-1) was found when MAP < 100 mm, which may be caused by long-term atmosphere deposition and the lack of biological uptake. The δ15N of soil nitrate increased with increasing MAP when MAP < 200 mm, and then decreased when MAP > 200 mm. The MAP accounted for 50% and 19% of the variation of the δ15N-NO3- values in these two distinguishable precipitation regions, respectively. Our results suggest that along this 3200-km grassland transect, when MAP > 200 mm, δ15N values of both ammonium and nitrate decrease with increasing precipitation and thus support the global δ15N pattern. However, under extreme aridity, biological and abiotic controls on soil N dynamics may yield different 15N pattern and such nonlinear response to precipitation should be further studied and incorporated into biogeochemical models.