Nitrous oxide fluxes determined by continuous eddy covariance measurements from intensively grazed pastures: Temporal patterns and environmental controls

被引:35
作者
Liang, Liyin L. [1 ,2 ,3 ]
Campbell, David I. [1 ,2 ]
Wall, Aaron M. [1 ,2 ]
Schipper, Louis A. [1 ,2 ]
机构
[1] Univ Waikato, Sch Sci, Private Bag 3105, Hamilton 3240, New Zealand
[2] Univ Waikato, Environm Res Inst, Private Bag 3105, Hamilton 3240, New Zealand
[3] Manaaki Whenua Landcare Res, Palmerston North 4442, New Zealand
关键词
Nitrous oxide; Eddy covariance; Water-filled pore space; Nitrification; Denitrification; Grazed pastures; QUANTUM CASCADE LASER; GREENHOUSE-GAS FLUXES; SOIL N2O FLUXES; NITRIFIER DENITRIFICATION; AEROBIC DENITRIFICATION; AGRICULTURAL SOILS; GRASSLAND SYSTEMS; CARBON BALANCE; URINE PATCH; EMISSIONS;
D O I
10.1016/j.agee.2018.09.010
中图分类号
S [农业科学];
学科分类号
09 ;
摘要
Nitrous oxide (N2O) is a prominent greenhouse gas. Our understanding of environmental controls on N2O fluxes has mainly come from small-scale experiments, for example, static chamber measurements on plots or lab incubations. However, studies of the environmental controls for N2O fluxes at ecosystem scales have been limited. Using eddy covariance (EC) measurements, this study evaluated the environmental drivers of N2O fluxes for a one-year period at a farm grazed year-round by daisy cows in the Waikato region, New Zealand. We identified an optimum soil moisture/temperature zone that favours maximal N2O emissions, demonstrating maximum N2O fluxes at 70% water-filled pore space (WFPS) and moderate soil temperatures. Our measurements consistently identified significant N2O flux pulses associated with rainfall following grazing events in warm-dry months. In contrast, during cold-wet months when WFPS was consistently high, pulses after rainfall did not occur. A clear positive temperature response for N2O fluxes was observed above 70% WFPS while a negative relationship was detected when WFPS was less than 70%. Distinctive diurnal flux patterns emerged in both pulses and background fluxes, implying that soil temperature regulates N2O fluxes at sub-daily timescales. Over the annual period, N2O emissions were 6.5 kg N2O-N ha(-1). We found the highest cumulative rates (maximum 35.7 g N2O-N ha(-1) day(-1)) in autumn but the rates were low during both summer and winter. Our results highlighted the combined effects of environmental factors on N2O fluxes, and quantified N2O flux variations at seasonal and daily scales, suggesting that continuous measurement techniques, such as EC, could serve as an alternative in national N2O inventories.
引用
收藏
页码:171 / 180
页数:10
相关论文
共 73 条
[21]   Nitrous oxide emissions from grazed grasslands: interactions between the N cycle and climate change - a New Zealand case study [J].
de Klein, Cecile A. M. ;
Shepherd, Mark A. ;
van der Weerden, Tony J. .
CURRENT OPINION IN ENVIRONMENTAL SUSTAINABILITY, 2014, 9-10 :131-139
[22]   Multiscale estimates of N2O emissions from agricultural lands [J].
Desjardins, R. L. ;
Pattey, E. ;
Smith, W. N. ;
Worth, D. ;
Grant, B. ;
Srinivasan, R. ;
MacPherson, J. I. ;
Mauder, M. .
AGRICULTURAL AND FOREST METEOROLOGY, 2010, 150 (06) :817-824
[23]   Nitrous oxide emission factors for agricultural soils in Great Britain: the impact of soil water-filled pore space and other controlling variables [J].
Dobbie, KE ;
Smith, KA .
GLOBAL CHANGE BIOLOGY, 2003, 9 (02) :204-218
[24]   Eddy covariance methane flux measurements over a grazed pasture: effect of cows as moving point sources [J].
Felber, R. ;
Muenger, A. ;
Neftel, A. ;
Ammann, C. .
BIOGEOSCIENCES, 2015, 12 (12) :3925-3940
[25]  
Firestone M. K., 1989, EXCHANGE TRACE GASES, P7, DOI DOI 10.1017/CBO9781107415324.004
[26]   Effects of climate and management intensity on nitrous oxide emissions in grassland systems across Europe [J].
Flechard, C. R. ;
Ambus, P. ;
Skiba, U. ;
Rees, R. M. ;
Hensen, A. ;
van Amstel, A. ;
van den Pol-van Dasselaar, A. ;
Soussana, J-F ;
Jones, M. ;
Clifton-Brown, J. ;
Raschi, A. ;
Horvath, L. ;
Neftel, A. ;
Jocher, M. ;
Ammann, C. ;
Leifeld, J. ;
Fuhrer, J. ;
Calanca, P. ;
Thalman, E. ;
Pilegaard, K. ;
Di Marco, C. ;
Campbell, C. ;
Nemitz, E. ;
Hargreaves, K. J. ;
Levy, P. E. ;
Ball, B. C. ;
Jones, S. K. ;
van de Bulk, W. C. M. ;
Groot, T. ;
Blom, M. ;
Domingues, R. ;
Kasper, G. ;
Allard, V. ;
Ceschia, E. ;
Cellier, P. ;
Laville, P. ;
Henault, C. ;
Bizouard, F. ;
Abdalla, M. ;
Williams, M. ;
Baronti, S. ;
Berretti, F. ;
Grosz, B. .
AGRICULTURE ECOSYSTEMS & ENVIRONMENT, 2007, 121 (1-2) :135-152
[27]   Bi-directional soil/atmosphere N2O exchange over two mown grassland systems with contrasting management practices [J].
Flechard, CR ;
Neftel, A ;
Jocher, M ;
Ammann, C ;
Fuhrer, J .
GLOBAL CHANGE BIOLOGY, 2005, 11 (12) :2114-2127
[28]  
Hewitt AE, 1998, NZ SOIL CLASSIFICATI
[29]   Greenhouse gas fluxes over managed grasslands in Central Europe [J].
Hoertnagl, Lukas ;
Barthel, Matti ;
Buchmann, Nina ;
Eugster, Werner ;
Butterbach-Bahl, Klaus ;
Diaz-Pines, Eugenio ;
Zeeman, Matthias ;
Klumpp, Katja ;
Kiese, Ralf ;
Bahn, Michael ;
Hammerle, Albin ;
Lu, Haiyan ;
Ladreiter-Knauss, Thomas ;
Burri, Susanne ;
Merbold, Lutz .
GLOBAL CHANGE BIOLOGY, 2018, 24 (05) :1843-1872
[30]   Estimation of nitrous oxide emission from Hungarian semi-arid sandy and loess grasslands; effect of soil parameters, grazing, irrigation and use of fertilizer [J].
Horvath, L. ;
Grosz, B. ;
Machon, A. ;
Tuba, Z. ;
Nagy, Z. ;
Czobel, S. Z. ;
Balogh, J. ;
Peli, E. ;
Foti, S. Z. ;
Weidinger, T. ;
Pinter, K. ;
Fuehrer, E. .
AGRICULTURE ECOSYSTEMS & ENVIRONMENT, 2010, 139 (1-2) :255-263