Soil N2O emissions after perennial legume termination in an alfalfa-wheat crop rotation system under Mediterranean conditions

被引:5
|
作者
Trozzo, Laura [1 ]
Francioni, Matteo [1 ,2 ]
Kishimoto-Mo, Ayaka Wenhong [2 ]
Foresi, Lucia [3 ]
Bianchelli, Michele [1 ]
Baldoni, Nora [1 ]
D'Ottavio, Paride [1 ]
Toderi, Marco [1 ]
机构
[1] Polytech Univ Marche, Dept Agr Food & Environm Sci, Ancona, Italy
[2] Natl Inst Agroenvironm Sci, Tsukuba, Ibaraki, Japan
[3] Natl Inst Agr Bot East Malling Res, New Rd, East Malling, Kent, England
关键词
Greenhouse gases; soil tillage; crop residues; nitrogen; NITROUS-OXIDE EMISSIONS; GREENHOUSE-GAS EMISSIONS; REDUCED-TILLAGE; WINTER-WHEAT; MANAGEMENT; MITIGATION; INPUT; AGRICULTURE; LANDSCAPE; RESIDUES;
D O I
10.4081/ija.2020.1613
中图分类号
S3 [农学(农艺学)];
学科分类号
0901 ;
摘要
Agricultural activities are potential sources of greenhouse gas (GHG) emissions, and nitrous oxide (N2O) is one of the most important non-carbon-dioxide GHGs. Perennial legumes such as alfalfa (Medicago sativa L.) have potential roles for reduction of soil GI IG emissions as part of crop rotation systems. However, the implications of perennial legume termination by tillage and subsequent soil incorporation of the residues for reduced 0110 emissions have been poorly examined in Mediterranean environments. With the aim to assess the magnitude of soil N2O emissions (important for the definition of mitigation strategies) after perennial legume termination in alfalfa-wheat crop rotation systems in a Mediterranean environment, we defined the hypothesis that alfalfa termination by tillage with incorporation of the crop residues will increase soil N2O emissions during the subsequent wheat season. To test this hypothesis, closed static chambers were used in a field-plot experiment, using a complete randomised block design with three replicates. Soil N2O emissions were monitored across 33 sampling dates from October 2017 to July 2018, as a comparison between an original 6-year-old alfalfa field ('continuous alfalfa') and alfalfa termination followed by wheat ('alfalfa+wheat'). The soil N2O emission fluxes varied markedly across the treatments and throughout the monitoring period (from -0.02 +/- 0.01 to 0.53 +/- 0.14 g N-N2O ha(-1) h(-1), and from 0.02 +/- 0.07 to 0.37 +/- 0.11 g N-N2O ha(-1) h(-1) for continuous alfalfa and alfalfa+wheat, respectively), generally following the changes in soil temperature. Several soil N2O emission peaks were recorded for both treatments, which mainly coincided with rainfall and with increased soil water content. In the 2 months following alfalfa termination, alfalfa-wheat showed higher cumulative weekly soil N2O emissions compared to continuous alfalfa. Following alfalfa termination for alfalfa-wheat, the increased cumulative weekly soil N2O emissions appeared to be due to asynchrony between nitrogen (N) released into the soil from mineralisation of the alfalfa residues and N uptake by the wheat. Despite these initial high soil N2O emissions for alfalfa+wheat, the seasonal cumulative soil N2O emissions were not significantly different (0.77 +/- 0.09 vs 0.85 +/- 0.18 kg N-N2O ha(-1) for continuous alfalfa and alfalfa-wheat, respectively). These data suggest that legume perennial crop termination in alfalfa-wheat rotation systems does not lead to significant loss of N2O from the soil. The alfalfa termination by tillage performed in autumn might, on the one hand, have slowed the mineralisation process, and might, on the other hand, have synchronised the N release by the mineralised crop residues, with the N uptake by the wheat reducing the soil N2O emissions.
引用
收藏
页码:229 / 238
页数:10
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