Controls and models for estimating direct nitrous oxide emissions from temperate and sub-boreal agricultural mineral soils in Europe

被引:69
作者
Freibauer, A
Kaltschmitt, M
机构
[1] Max Planck Inst Biogeochem, D-07701 Jena, Germany
[2] Inst Energet & Umwelt gGmbH, D-04347 Leipzig, Germany
关键词
arable land; crop; denitrification; emission factor; Europe; fertiliser; grassland; model; nitrogen; nitrous oxide; soil;
D O I
10.1023/A:1023398108860
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
Based on a review of N2O field studies in Europe, major soil, climate and management controls of N2O release from agricultural mineral soils in the European Union have been identified. Data for these N2O emission drivers can easily be gathered from statistical services. Using stepwise multivariate linear regression analysis, empirical first order models of N2O emissions have been established which allow - in contrast to existing large-scale approaches - a regionally disaggregated estimation of N2O emissions at sub-national, national and continental level in the temperate and boreal climate regions of Europe. Arable soils showed lower mean and maximum emissions in oceanic temperate climate ("Temperate West") than in pre-alpine temperate and sub-boreal climate ("Sub-boreal Europe"). Therefore, two separate regression models were developed. Nitrous oxide emissions from arable soils the Temperate West amount to an average flux rate below 2 kg N2O-N ha(-1) yr(-1) and rarely exceed 5 kg N2O-N ha(-1) yr(-1). They are modelled by the parameters fertiliser, topsoil organic carbon and sand content. In Sub-boreal European arable soils, N2O emissions vary in a much wider range between 0 and 27 kg N2O-N ha(-1) yr(-1) in dependence of available nitrogen, represented in the model by fertiliser and topsoil nitrogen content. Compared to existing methods for large scale inventories, the regression models allow a better regional fit to measured values since they integrate additional driving forces for N2O emissions. For grasslands, a fertiliser-based model was established which yields higher emission estimates than existing ones. Due to an extreme variability, no climate, soil nor management parameters could be included in the empirical grasslands model.
引用
收藏
页码:93 / 115
页数:23
相关论文
共 66 条
[1]   Nitrous oxide emissions from soils due to inputs of nitrogen from excreta return by livestock on grazed grassland in the UK [J].
Allen, AG ;
Jarvis, SC ;
Headon, DM .
SOIL BIOLOGY & BIOCHEMISTRY, 1996, 28 (4-5) :597-607
[2]   SPATIAL AND SEASONAL NITROUS-OXIDE AND METHANE FLUXES IN DANISH FOREST-ECOSYSTEMS, GRASSLAND-ECOSYSTEMS, AND AGROECOSYSTEMS [J].
AMBUS, P ;
CHRISTENSEN, S .
JOURNAL OF ENVIRONMENTAL QUALITY, 1995, 24 (05) :993-1001
[3]  
[Anonymous], SOIL USE MANAGE
[4]  
[Anonymous], ASA SPECIAL PUBLICAT
[5]   The effect of urea and pig slurry fertilization on denitrification, direct nitrous oxide emission, volatile fatty acids, water-soluble carbon and anthrone-reactive carbon in maize-cropped soil from the Po plain (Modena, Italy) [J].
Arcara, PG ;
Gamba, C ;
Bidini, D ;
Marchetti, R .
BIOLOGY AND FERTILITY OF SOILS, 1999, 29 (03) :270-276
[7]   KINETIC EXPLANATION FOR ACCUMULATION OF NITRITE, NITRIC-OXIDE, AND NITROUS-OXIDE DURING BACTERIAL DENITRIFICATION [J].
BETLACH, MR ;
TIEDJE, JM .
APPLIED AND ENVIRONMENTAL MICROBIOLOGY, 1981, 42 (06) :1074-1084
[8]   Direct emission of nitrous oxide from agricultural soils [J].
Bouwman, AF .
NUTRIENT CYCLING IN AGROECOSYSTEMS, 1996, 46 (01) :53-70
[9]   Sources of nitrous oxide in soils [J].
Bremner, JM .
NUTRIENT CYCLING IN AGROECOSYSTEMS, 1997, 49 (1-3) :7-16
[10]   PROFILE NITROUS-OXIDE AND CARBON-DIOXIDE CONCENTRATIONS IN A SOIL SUBJECT TO FREEZING [J].
BURTON, DL ;
BEAUCHAMP, EG .
SOIL SCIENCE SOCIETY OF AMERICA JOURNAL, 1994, 58 (01) :115-122