Home > Publications database > Nitrate leaching, direct and indirect nitrous oxide fluxes from sloping cropland in the purple soil area, southwestern China > print

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|a pmid:22243886
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|a 10.1016/j.envpol.2011.12.001
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|a Environmental Sciences
100 1 _ |0 P:(DE-HGF)0
|a Zhou, M.
|b 0
245 _ _ |a Nitrate leaching, direct and indirect nitrous oxide fluxes from sloping cropland in the purple soil area, southwestern China
260 _ _ |a Amsterdam [u.a.]
|b Elsevier Science
|c 2012
300 _ _ |a 361 - 368
336 7 _ |a Journal Article
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440 _ 0 |0 8083
|a Environmental Pollution
|v 162
|x 0269-7491
500 _ _ |3 POF3_Assignment on 2016-02-29
500 _ _ |a This study was gratefully supported by National Program on Key Basic Research Plan of China (Grant No. 2012CB417101), the National Science & Technology Pillar Program (Grant No. 2011BAD31B03), the Helmholtz-CAS Joint Laboratory ENTRANCE and the Natural Science Foundation of China (Grant No. 40901144). Furthermore, we sincerely thank Mr. Yanqiang Wang, Zebin Zeng and other staff at Yanting station for their support in the field measurements.
520 _ _ |a This study provides a combined dataset on N loss pathways and fluxes from sloping cropland in the purple soil area, southwestern China. A lysimeter experiment was conducted to quantify nitrate leaching (May 2004-May 2010) and N(2)O emission (May 2009-May 2010) losses. Nitrate leaching was the dominant N loss pathway and annual leaching fluxes ranged from 19.2 to 53.4 kg N ha(-1), with significant differences between individual observation years (P < 0.05). Direct N(2)O emissions due to N fertilizer use were 1.72 ± 0.34 kg N ha(-1) yr(-1), which corresponds to an emission factor of 0.58 ± 0.12%. However, indirect N(2)O emissions caused by nitrate leaching and surface runoff N losses, may contribute another 0.15-0.42 kg N ha(-1) yr(-1). Our study shows that nitrate leaching lowered direct N(2)O emissions, highlighting the importance for a better understanding of the tradeoff between direct and indirect N(2)O emissions for the development of meaningful N(2)O emission strategies.
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650 _ 2 |2 MeSH
|a China
650 _ 2 |2 MeSH
|a Environmental Monitoring
650 _ 2 |2 MeSH
|a Fertilizers: analysis
650 _ 2 |2 MeSH
|a Nitrates: analysis
650 _ 2 |2 MeSH
|a Nitrogen Cycle
650 _ 2 |2 MeSH
|a Nitrous Oxide: analysis
650 _ 2 |2 MeSH
|a Soil: analysis
650 _ 7 |0 0
|2 NLM Chemicals
|a Fertilizers
650 _ 7 |0 0
|2 NLM Chemicals
|a Nitrates
650 _ 7 |0 0
|2 NLM Chemicals
|a Soil
650 _ 7 |0 10024-97-2
|2 NLM Chemicals
|a Nitrous Oxide
650 _ 7 |2 WoSType
|a J
653 2 0 |2 Author
|a Nitrate leaching
653 2 0 |2 Author
|a Direct N2O emission
653 2 0 |2 Author
|a Indirect N2O emission
653 2 0 |2 Author
|a Sloping cropland
653 2 0 |2 Author
|a Purple soil
700 1 _ |0 P:(DE-HGF)0
|a Zhu, B.
|b 1
700 1 _ |0 P:(DE-HGF)0
|a Butterbach-Bahl, K.
|b 2
700 1 _ |0 P:(DE-HGF)0
|a Wang, T.
|b 3
700 1 _ |0 P:(DE-HGF)0
|a Bergmann, J.
|b 4
700 1 _ |0 P:(DE-Juel1)142357
|a Brüggemann, N.
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|u FZJ
700 1 _ |0 P:(DE-HGF)0
|a Wang, Z.
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700 1 _ |0 P:(DE-HGF)0
|a Li, T.
|b 7
700 1 _ |0 P:(DE-HGF)0
|a Kuang, F.
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773 _ _ |0 PERI:(DE-600)2013037-5
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|g Vol. 162, p. 361 - 368
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|q 162<361 - 368
|t Environmental pollution
|v 162
|x 0269-7491
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856 7 _ |u http://dx.doi.org/10.1016/j.envpol.2011.12.001
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