Nitrous oxide and nitric oxide emissions from maize field plots as affected by N fertilizer type and application method

被引:43
作者
Yan, XY [1 ]
Hosen, Y [1 ]
Yagi, K [1 ]
机构
[1] Japan Int Res Ctr Agr Sci, Tsukuba, Ibaraki 3058686, Japan
关键词
nitrous oxide; nitric oxide; nitrogen fertilizer; application method; mitigation;
D O I
10.1007/s003740100401
中图分类号
S15 [土壤学];
学科分类号
0903 ; 090301 ;
摘要
NO and NO emissions from an Andisol maize field were studied. The experimental treatments were incorporation of urea into the plough layer at 250 kg N ha(-1) by two applications (U1250), band application of urea at a depth of 8 cm at 75 kg N ha(-1) plus incorporation of urea into the plough layer at 75 kg N ha(-1) (UB150), band application of polyolefin-coated urea at a depth of 5 cm at 150 kg N ha(-1) (CB150), and a control (without N application). N2O fluxes from U1250 and UB 150 peaked following the incorporation of supplementary fertilizer, and declined to the background level after that, while the NO flux from CB 150 was relatively low but remained at constant level until shortly after harvest. Accordingly, the total N2O emissions during the whole cultivation period from the three treatments were not significantly different. The fertilizer-derived N2O-N losses from U1250, UB150 and CB150 were 0.15%, 0.27% and 0.28% of the applied N, respectively. However, it was suggested that, due to the low plant N recovery, U1250 had a significantly larger potential for indirect N2O emission than the other treatments. On the other hand, NO emissions from U1250 and UB 150 were 12 times higher than that from CB 150, and the fertilizer-derived NO-N losses from the three treatments were 0.16%, 0.27% and 0.026% of the applied N, respectively. Significant NO fluxes were detected only when urea-N fertilizer was surface-applied and incorporated into plough-layer soil.
引用
收藏
页码:297 / 303
页数:7
相关论文
共 31 条
[1]  
AKIYAMA H, 1998, RES REP DIV ENV PLAN, V14, P39
[2]   RELATIVE RATES OF NITRIC-OXIDE AND NITROUS-OXIDE PRODUCTION BY NITRIFIERS, DENITRIFIERS, AND NITRATE RESPIRERS [J].
ANDERSON, IC ;
LEVINE, JS .
APPLIED AND ENVIRONMENTAL MICROBIOLOGY, 1986, 51 (05) :938-945
[3]   ACETYLENE AND N-SERVE EFFECTS UPON N2O EMISSIONS FROM NH-4+ AND NO-3- TREATED SOILS UNDER AEROBIC AND ANAEROBIC CONDITIONS [J].
AULAKH, MS ;
RENNIE, DA ;
PAUL, EA .
SOIL BIOLOGY & BIOCHEMISTRY, 1984, 16 (04) :351-356
[4]   An international cooperative programme indicates the widespread occurrence of ozone injury on crops [J].
Benton, J ;
Fuhrer, J ;
Gimeno, BS ;
Skärby, L ;
Palmer-Brown, D ;
Ball, G ;
Roadknight, C ;
Mills, G .
AGRICULTURE ECOSYSTEMS & ENVIRONMENT, 2000, 78 (01) :19-30
[5]  
BOLLE HJ, 1986, SCOPE, V29, P157
[6]   EFFECT OF NITRAPYRIN ON EMISSION OF NITROUS-OXIDE FROM SOIL FERTILIZED WITH ANHYDROUS AMMONIA [J].
BREMNER, JM ;
BREITENBECK, GA ;
BLACKMER, AM .
GEOPHYSICAL RESEARCH LETTERS, 1981, 8 (04) :353-356
[7]   NITROUS-OXIDE EMISSIONS IN IRRIGATED CORN AS AFFECTED BY NITRIFICATION INHIBITORS [J].
BRONSON, KF ;
MOSIER, AR ;
BISHNOI, SR .
SOIL SCIENCE SOCIETY OF AMERICA JOURNAL, 1992, 56 (01) :161-165
[10]   SOURCES OF NITRIC-OXIDE AND NITROUS-OXIDE FOLLOWING WETTING OF DRY SOIL [J].
DAVIDSON, EA .
SOIL SCIENCE SOCIETY OF AMERICA JOURNAL, 1992, 56 (01) :95-102