全球N_2O年释放总量及各类源相对贡献率初步分析

根据国际上最近确定的全球N2 O各释放源及其释放量估算值 ,推算了全球N2 O年释放总量及各类源的相对贡献率。得出全球N2 O年释放总量约 1 4 .7TgN2 O -N ,其中自然源和人为源分别占 57%和 4 3 %。年释放总量中N的生物地球化学过程约贡献92 %、非生物作用过程仅贡献 8% ;与土壤有关的释放源约贡献 70 %、农业土壤贡献2 0 %。控制土壤尤其是农业土壤和热带森林土壤的N2 O释放量是控制全球大气N2 O浓度上升的关键     

有机肥与无机肥配施对潮土N2O排放的影响

华北平原是我国重要的粮食主产区,由于土壤有机质含量低,增加氮肥用量并不能导致玉米产量持续增加.有机肥和无机肥配施被广泛认为是同时实现粮食增产和提高土壤有机质的双赢措施,但是有机肥和无机肥配施对华北平原农田N_2O排放的影响尚不明确.本研究在华北平原潮土区,通过测定不同种类有机肥与无机肥配施后农田N_2O排放通量和作物产量,旨在揭示不同种类有机肥及其用量对潮土N_2O排放和作物产量的影响效应.田间试验共设置8个处理,分别为不施肥(CK)、化肥氮(NPK)、 40%牛粪氮+60%化肥氮(CM)、 40%鸡粪氮+60%化肥氮(FC)、 40%猪粪氮+60%化肥氮(FP)、 20%牛粪氮+80%化肥氮(1/2CM)、 20%鸡粪氮+80%化肥氮(1/2FC)和20%猪粪氮+80%化肥氮(1/2FP).整个玉米季N_2O排放通量均与土壤WFPS显著正相关(P0.05).除NPK处理外,玉米季N_2O排放量与土壤可溶性有机碳(DOC)平均含量存在显著的线性关系.玉米季CK处理N_2O排放量为0.50 kg·hm~(-2),NPK处理增加到2.28 kg·hm~(-2).相同用量不同种类有机肥处理,N_2O排放未出现显著差异. 40%有机肥氮用量处理下N_2O排放量与NPK处理无显著差异,而用量减少至20%后, 1/2CM、 1/2FC和1/2FP处理N_2O排放量分别较CM、 FC和FP减少了33.6%、 43.7%和12.1%,其主要原因为易分解有机碳输入减少,土壤DOC含量降低,但玉米产量未出现显著差异.因此,从减少温室效应的角度,玉米季80%化肥氮配施20%有机肥氮为本地区农田施肥的较佳选择.     

Nitrous oxide emissions from a maize field during two consecutive growing seasons in the North China Plain

Nitrous oxide (N₂O) emissions from a maize field in the North China Plain (Wangdu County, Hebei Province, China) were investigated using static chambers during two consecutive maize growing seasons in the 2008 and 2009. The N₂O pulse emissions occurred with duration of about 10 days after basal and additional fertilizer applications in the both years. The average N₂O fluxes from the CK (control plot, without crop, fertilization and irrigation), NP (chemical N fertilizer), SN (wheat straw returning plus chemical N fertilizer), OM- 1/2N (chicken manure plus half chemical N fertilizer) and OMN (chicken manure plus chemical N fertilizer) plots in 2008 were 8.51, 72.1, 76.6, 101, 107 ng N/(m²·sec), respectively, and in 2009 were 33.7, 30.0 and 35.0 ng N/(m²·sec) from CK, NP and SN plots, respectively. The emission factors of the applied fertilizer as N₂O-N (EFs) were 3.8% (2008) and 1.1% (2009) for the NP plot, 3.2% (2008) and 1.2% (2009) for the SN plot, and 2.8% and 2.2% in 2008 for the OM-1/2N and OMN plots, respectively. Hydromorphic properties of the investigated soil (with gley) are in favor of denitrification. The large differences of the soil temperature and water-filled pore space (WFPS) between the two maize seasons were suspected to be responsible for the significant yearly variations. Compared with the treatments of NP and SN, chicken manure coupled with compound fertilizer application significantly reduced fertilizer loss rate as N₂O-N.     

Effects of long-term amendment of organic manure and nitrogen fertilizer on nitrous oxide emission in a sandy loam soil

To understand the effects of long-term amendment of organic manure and N fertilizer on N2O emission in the North China Plain, a laboratory incubation at different temperatures and soil moistures were carried out using soils treated with organic manure （OM）, half organic manure plus half fertilizer N （HOM）, fertilizer NPK （NPK）, fertilizer NP （NP）, fertilizer NK （NK）, fertilizer PK （NK） and control （CK） since 1989. Cumulative N2O emission in OM soil during the 17 d incubation period was slightly higher than in NPK soil under optimum nitrification conditions （25℃ and 60% water-filled pore space, WFPS）, but more than twice under the optimum denitrification conditions （35℃ and 90% WFPS）. N2O produced by denitrification was 2.1-2.3 times greater than that by nitrification in OM and HOM soils, but only 1.5 times greater in NPK and NP soils. These results implied that the long-term amendment of organic manure could significantly increase the N2O emission via denitrification in OM soil as compared to NPK soil. This is quite different from field measurement between OM soil and NPK soil. Substantial inhibition of the formation of anaerobic environment for denitrification in field might result in no marked difference in N2O emission between OM and NPK soils. This is due in part to more rapid oxygen diffusion in coarse textured soils than consumption by aerobic microbes until WFPS was 75% and to low easily decomposed organic C of organic manure. This finding suggested that addition of organic manure in the tested sandy loam might be a good management option since it seldom caused a burst of N2O emission but sequestered atmospheric C and maintained efficiently applied N in soil.     

Nitrogen transformation in maize soil after application of different organic manures

IntroductionAnimalwastesareusuallyappliedtosoilasorganicmanure .Applicationoforganicmanuretoarablelandisrecommendedforrecyclingvaluablenutrientresources .However ,ifimproperlyused ,organicmanuremaybecomeasourceofenvironmentalproblems ,suchasgreenhousegasemissions ,ammoniavolatilizationandNO- 3 Nleachingintogroundwater (Williams ,1999) .Nitrateleachingfromarableland ,whichcausescontaminationofgroundwater,hasbecomeamatterofworldwideconcern .Therearemanydocumentsontheeffectsofchemicalfertilizer…     

Modelling impacts of alternative farming management practices on greenhouse gas emissions from a winter wheat–maize rotation system in China

Agricultural production plays an important role in affecting atmospheric greenhouse gas concentrations. Field measurements were conducted in Quzhou County, Hebei Province in the North China Plains to quantify carbon dioxide (CO₂) and nitrous oxide (N₂O) emissions from a winter wheat–maize rotation field, a common cropping system across the Chinese agricultural regions. The observed flux data in conjunction with the local climate, soil and management information were utilized to test a process-based model, Denitrification–Decomposition or DNDC, for its applicability for the cropping system. The validated DNDC was then used for predicting impacts of three management alternatives (i.e., no-till, increased crop residue incorporation and reduced fertilizer application rate) on CO₂ and N₂O emissions from the target field. Results from the simulations indicated that (1) CO₂ emissions were significantly affected by temperature, initial SOC, tillage method, and quantity and quality of the organic matter added in the soils; (2) increases in temperature, initial SOC, total fertilizer N input, and manure amendment substantially increased N₂O emissions; and (3) temperature, initial SOC, tillage, and quantity and quality of the organic matter added in the soil all had significant effects on global warming. Finally, five 50-year scenarios were simulated with DNDC to predict their long-term impacts on crop yield, soil C dynamics, nitrate leaching losses, and N₂O emissions. The modelled results suggested that implementation of manure amendment or crop residue incorporation instead of increased fertilizer application rates would more efficiently mitigate GHG emissions from the tested agro-ecosystem. The multi-impacts provided a sound basis for comprehensive assessments on the management alternatives.     

中国地区氧化亚氮排放量及其变化的估算

对我国大气中氧化亚氮的排放源及其大小进行了分析和计算,中国地区氧化亚氮的年排放置为950G_9N_2O-N,约占全球总排放量的6％.天然源和人为源各占我国氧化亚氮排放量的71％和29％.在天然源中以海洋排放为主,人为源中则以煤炭燃烧释放的贡献最大.计算显示今后几年内氧化亚氮排放的年增加量是6G_9N_2O-N.     

Nitrous oxide emissions from organic and conventional crop rotations in five European countries

Nitrous oxide (N₂O) emissions from agriculture are currently estimated from N inputs using emission factors, and little is known about the importance of regional or management-related differences. This paper summarizes the results of a study in which N₂O emission rates were recorded on 15–26 occasions during a 12-month period in organic and conventional dairy crop rotations in five European countries (Austria, Denmark, Finland, Italy, UK). A common methodology based on static chambers was used for N₂O flux measurements, and N₂O data were compiled together with information about N inputs (from fertilizers, N₂ fixation, atmospheric deposition and excretal returns), crop rotations and soil properties. Organic rotations received only manure as N fertilizer, while manure accounted for 0–100% of fertilizer N in conventional rotations. A linear regression model was used to examine effects of location, system and crop category on N₂O emissions, while a second model examined effects of soil properties. Nitrous oxide emissions were higher from conventional than from organic crop rotations except in Austria and, according to the statistical analysis, the differences between locations and crop categories were significant. Ammonium was significantly related to N₂O emissions, although this effect was dominated by observations from a grazing system. Despite the limited number of samplings, annual emissions were estimated by interpolation. Across the two systems and five locations there was a significant relationship between total N inputs and N₂O emissions at the crop rotation level which indicated that annually 1.6 ± 0.2% (mean ± standard error) of total N inputs were lost as N₂O, while there was a background emission of 1.4 ± 0.3 kg N₂O-N ha⁻¹ year⁻¹. Although this measurement program emphasized system effects at the expense of high temporal resolution, the results indicate that N input is a significant determinant for N₂O emissions from agricultural soils.     

我国农田土壤的主要温室气体CO2、CH4和N2O排放研究

讨论土壤主要温室体ＣＯ２,ＣＨ４和Ｎ２Ｏ的排放过程,计算我国农田生态系统排放ＣＯ２、ＣＨ４和Ｎ２Ｏ的总量。１９９０年,中国地区ＣＯ２、ＣＨ４和Ｎ２Ｏ农田排放源强分别是２６０ＴｇＣＯ２,１７．５ＴｇＣｈ４和０．０９６ＴｇＮ,它们占我国相应这些气体排放量的８％,５０％和１０％,论述了温室气体浓度增加可能以农业产生的影响及应采取的控制对策。     

Direct nitrous oxide emissions from agricultural fields in China estimated by the revised 1996 IPPC guidelines for national greenhouse gases

Using revised 1996 IPCC guidelines for national greenhouse gases and statistic data in China Agricultural Yearbook, we estimated the direct nitrous oxide (N₂O) emissions from agricultural fields in China for the following years: 1949, 1954, 1960, 1965, 1970, 1975, 1980, 1985, 1990 and 1995. Direct N₂O emissions have been increasing continuously, from 26 Gg N in 1949 to 336 Gg N in 1995, at a rate of 7 Gg N y⁻¹. The main reason for the rapid increase in N₂O emissions was the increase in the use of synthetic fertilizer, which contributed 0.28% to the total emissions from soils in 1949, compared with 73.7% in 1990.Modifications to some equations and parameters were made according the local agricultural practices, such as the type of crops, the use of crop residue, cultivation of leguminous green manure and the application of animal manure as fertilizer in China. The trend of direct N₂O emissions from agricultural fields in China is discussed in this paper.     

生物炭和有机肥对菜地土壤N2O排放及硝化、反硝化微生物功能基因丰度的影响

通过室内培养试验和实时荧光定量PCR技术,研究了田间施用生物炭和有机肥对菜地土壤氧化亚氮(N_2O)排放、氨单加氧酶(amo A)和亚硝酸盐还原酶(nir S、nir K)、氧化亚氮还原酶(nos Z)基因丰度的影响,并探讨功能基因丰度对N_2O排放的影响.试验设置5个处理:CK(对照)、N(尿素)、N+BC(尿素和生物炭)、N+M(尿素和有机肥)和N+BC+M(尿素、生物炭和有机肥).结果表明,与CK处理相比,各施肥处理均降低了土壤氨氧化细菌(AOB)和氨氧化古菌(AOA)丰度,增加了nir K、nir S和nos Z基因丰度,并提高了培养期间N_2O累积排放量.与N处理相比,N+BC处理的土壤p H值提高了11.1%,并增加了AOB、AOA、nir S、nir K和nos Z基因丰度,增幅分别为105.8%、57.3%、22.0%、176.2%和204.9%,同时显著降低了培养期间N_2O累积排放量,降幅为58.1%;N+M处理增加了nir K和nir S基因丰度,增幅分别为58.8%和7.1%,对N_2O排放的影响不显著;N+BC+M处理增加了AOB、nir K、nir S和nos Z基因丰度,增幅分别为30.7%、68.7%、6.5%和84.5%,降低了N_2O累积排放量,降幅为14.4%.生物炭通过增加amo A、nir S和nir K基因丰度间接增加N_2O排放,同时通过增加nos Z基因丰度促进N_2O还原,综合效应表现为降低了菜地土壤N_2O排放.因此,通过施用生物炭改善土壤性质,增加功能基因丰度,降低土壤N_2O排放,是一种较好的N_2O减排措施.施用有机肥可以增加反硝化作用功能基因丰度,但对N_2O减排效果不显著.     

猪粪化肥配施对双季稻田CH4和N2O排放及其全球增温潜势的影响

以湖南典型红壤双季稻田系统为研究对象,采用静态箱-气相色谱法研究了水稻生长季基肥配施猪粪条件下CH4和N2O的排放特征,并估算了排放的CH4和N2O的全球增温潜势(GWP).结果表明,与施用化肥处理相比,猪粪化肥配施对稻田CH4和N2O排放的季节变化模式无明显影响,但影响其排放量大小.两个稻季,猪粪替代50%化学氮肥处理(1/2N+PM)CH4累积排放量较不施氮肥处理(0N)、50%化学氮肥处理(1/2N)、100%化学氮肥处理(N)分别提高54.83%、33.85%和43.30%(P<0.05);1/2N+PM处理N2O累积排放量较N处理显著降低67.50%,较0N处理、1/2N处理分别提高129.43%、119.23%(P<0.05).水稻生长季CH4是GWP的主要贡献者,占CH4和N2O综合GWP的99%以上.1/2N+PM处理的GWP显著高于其他处理(P<0.05),且1/2N+PM处理单位产量GWP最高,较N处理、1/2N处理、0N处理分别提高58.21%、26.82%、20.63%.因此,双季稻田猪粪替代部分化学氮肥较全部施用化学氮肥增加了双季稻田CH4和N2O排放的综合温室效应,其对温室气体排放的影响需在区域温室气体排放清单中加以考虑.     

种植绿肥对作物产量和细菌群落稳定性的影响

为深入研究青海高原地区长期种植绿肥,减施化肥条件下小麦/油菜产量及土壤理化性状及微生物群落的变化,通过2011年建立的定位试验,设GF0（毛苕子作为绿肥,不施用化肥）、GF60（毛叶苕子配施60%化肥）、GF70（毛叶苕子配施70%化肥）、GF80（毛叶苕子配施80%化肥）、GF90（毛叶苕子配施90%化肥）、GF100（毛叶苕子配施100%化肥）、F0（休耕并且不施化肥）、F100（休耕并且施用100%化肥）共8个处理,利用高通量测序等技术,研究了种植利用绿肥减施化肥条件下小麦和油菜的产量、土壤性质和微生物群落结构的变化特征.结果表明,在保证小麦、油菜不减产的基础上,种植绿肥后茬作物减施化肥达到30%左右.绿肥配施减量化肥对土壤肥力有显著的提升作用,特别是土壤有机碳和全氮含量有明显的提高,分别提高1.34%~7.46%、2.16%~7.48%.化肥与绿肥配施增强了土壤微生物群落多样性,其中酸杆菌门和变形菌门是本研究土壤中的优势菌群.共生网络分析表明,绿肥处理提高了细菌群落的稳定性和抗干扰能力,同时绿肥应用增加了细菌群落中的关键物种.本研究表明,不同土壤微生物丰度受种植模式、施肥量影响很大,长期种植绿肥、减施化肥提高了土壤微生物丰度和多样性,增强微生物群落的稳定性.种植绿肥条件下化肥减肥量30%左右保证作物稳产可为当地的施肥管理提供参考.     

菜地氨氧化微生物驱动的N2O和NO对有机无机肥配施的响应

氨氧化细菌（AOB）和氨氧化古菌（AOA）是驱动土壤氨氧化过程的"引擎".氨氧化过程在土壤氧化亚氮（N₂O）和一氧化氮（NO）排放过程中扮演着重要角色.有机无机肥配施是实现化肥零增长和作物稳产增产的重要途径，但在有机无机肥配施下，菜地土壤AOB和AOA对氨氧化过程的相对贡献仍不清楚.本研究采用选择性抑制的方法（辛炔和乙炔）区分有机肥添加近3年后（2016年10月—2019年5月）AOB和AOA在氨氧化过程中对碱性菜地土壤N₂O和NO产生的相对贡献.试验共设5种施肥处理：不施氮肥（CK）、单施尿素（N）、单施有机肥（M）、50%尿素+50%有机肥（M1N1）和80%尿素+20%有机肥（M1N4）.结果表明，有机无机肥配施（M1N1和M1N4）可显著增加土壤电导率、有机碳和全氮含量.培养试验发现，与N处理相比，M和M1N1处理分别使N₂O排放量增加100.7%和38.8%，NO排放量增加77.9%和42.8%，AOB基因丰度增加16.6%和10.2%，同时，AOB对N₂O排放的相对贡献增加6.5%.相反，M1N4处理分别使N₂O和NO排放量降低19.3%和4.8%，AOB基因丰度降低37.5%，同时，AOB对N₂O及NO排放的相对贡献分别降低7.8%和7.4%.相关分析表明，土壤N₂O和NO累积排放量与土壤AOB基因丰度呈显著正相关（p<0.05），与土壤AOA基因丰度无显著相关性.有机无机肥配施下AOB是氨氧化过程的主要驱动者，适当比例的有机无机肥配施（即M1N4）措施可在一定程度上减弱AOB对碱性菜地土壤N₂O及NO排放的相对贡献.     

Nitrous oxide emissions from black soils with different pH

N₂O fluxes as a function of incubation time from soil with different available N contents and pH were determined. Cumulative carbon dioxide (CO₂) emissions were measured to indicate soil respiration. A 144-hr incubation experiment was conducted in a slightly acidic agricultural soil (pH_H2O 5.33) after the pH was adjusted to four different values (3.65, 5.00, 6.90 and 8.55). The experiments consisted of a control without added N, and with NH₄⁺-N and NO₃^--N fertilization. The results showed that soil pH contributed significantly to N₂O flux from the soils. There were higher N₂O emissions in the period 0-12 hr in the four pH treatments, especially those enhanced with N-fertilization. The cumulative N₂O-N emission reached a maximum at pH 8.55 and was stimulated by NO₃^--N fertilization (70.4 μg/kg). The minimum emissions appeared at pH 3.65 and were not stimulated by NO₃^--N or NH₄⁺-N fertilization. Soil respiration increased significantly due to N-fertilization. Soil respiration increased positively with soil pH (R² = 0.98, P < 0.01). The lowest CO₂-C emission (30.2 mg/kg) was presented in pH 3.65 soils without N-fertilization. The highest CO₂-C emissions appeared in the pH 8.55 soils for NH₄⁺-N fertilization (199 mg/kg). These findings suggested that N₂O emissions and soil respiration were significantly influenced by low pH, which strongly inhibits soil microbial nitrification and denitrification activities. The content of NO₃^--N in soil significantly and positively affected the N₂O emissions through denitrification.     

Effects of cultivation on N2O emission and seasonal quantitative variations of related microbes in a temperate grassland soil

ＩｎｔｒｏｄｕｃｔｉｏｎＡｔｍｏｓｐｈｅｒｉｃｎｉｔｒｏｕｓｏｘｉｄｅ (Ｎ2 Ｏ)ｉｓａｖｅｒｙｒａｄｉｏａｃｔｉｖｅｌｙａｃｔｉｖｅｇｒｅｅｎｈｏｕｓｅｇａｓ,ａｌｓｏｃｏｎｔｒｉｂｕｔｉｎｇｔｏｔｈｅｄｅｐｌｅｔｉｏｎｏｆｏｚｏｎｅｌａｙｅｒｏｆｓｔｒａｔｏｓｐｈｅｒｅ .ＡｔｍｏｓｐｈｅｒｉｃＮ2 Ｏｍａｉｎｌｙｏｒｉｇｉｎａｔｅｄｆｒｏｍｎｉｔｒｉｆｉｃａｔｉｏｎａｎｄｄｅｎｉｔｒｉｆｉｃａｔｉｏｎｉｎｔｅｒｒｅｓｔｒｉａｌｅｃｏｓｙｓｔｅｍｓ.Ｇｒａｓｓｌａｎｄｅｃｏｓｙｓｔｅｍ ,ａｃｃｏｕｎ…     

稻田不同种类有机肥施用对后季麦田N2O排放的影响

以稻麦轮作系统为对象,研究水稻生长季基肥施用不同有机物料对后季麦田N₂O排放及年轮作系统CH₄和N₂O综合温室效应的影响.结果表明:与施用化肥(化肥处理)相比,施用菜饼加化肥(菜饼处理)对后季麦田N₂O排放量无影响;施用小麦秸秆加化肥(小麦秸秆处理)导致后季麦田的N₂O排放量减少15%;施用牛厩肥加化肥(牛厩肥处理)和猪厩肥加化肥(猪厩肥处理)分别增加29%和16%.就稻麦年轮作生长季总体而言,菜饼、牛厩肥和猪厩肥处理稻麦生长季N₂O排放总量较化肥处理分别增加6%、17%和7%,然而,小麦秸秆处理N₂O排放总量减少16%.20a或500a时间尺度上各处理稻田CH₄排放和该轮作周期水稻和小麦生长季N₂O排放的总GWP值由大到小的顺序分别为:菜饼处理>小麦秸秆处理>牛厩肥处理>猪厩肥处理>化肥处理或菜饼处理>牛厩肥处理>猪厩肥处理>小麦秸秆处理>化肥处理.单位产量的GWP以作物残体处理最高,农家肥其次,化肥处理最低.因此,稻田基施不同种类有机物料都相应地增加稻麦轮作系统CH₄和N₂O排放的综合温室效应.     

Effect of different fertilizers on methane emission from a paddy field of Zhejiang, China

ＩｎｔｒｏｄｕｃｔｉｏｎＩｎｃｒｅａｓｅｄａｇｒｉｃｕｌｔｕｒａｌｐｒｏｄｕｃｔｉｖｉｔｙｏｖｅｒｔｈｅｐａｓｔ５０—１００ｙｅａｒｓｈａｓｌｅｄｔｏｉｎｃｒｅａｓｅｄａｔｍｏｓｐｈｅｒｉｃｃｏｎｃｅｎｔｒａｔｉｏｎｓｏｆＣＯ２，ＣＨ４ａｎｄＮ２Ｏ．Ｔｈｅｓｅｇａｓｅｓ，ａｌｏｎｇｗｉｔｈａｄｄｉｔｉｏｎｔｒａｃｅｇａｓｓｐｅｃｉｅｓ（ｇｒｅｅｎｈｏｕｓｅｇａｓｅｓ）ａｒｅｃａｕｓｉｎｇａｎｉｎｃｒｅａｓｅｉｎｇｌｏｂａｌｔｅｍｐｅｒａｔｕｒｅｓａｎｄｏｚｏｎｅｄｅｐｌｅｔｉｏｎ（Ａｓｅｌｍａｎ…     

不同水分管理方式下水稻生长季N2O排放量估算：模型应用

基于田间原位测定结果,作者建立了不同水分管理方式下稻田N₂O排放估算的统计模型. 在模型验证和输入参数检验的基础上, 本研究应用模型估算了20世纪50～90年代我国稻田水稻生长季N₂O直接排放量. 结果表明, 由于水稻种植面积和氮输入量的增加、以及水分管理方式的变化, 稻田N₂O-N季节排放量从20世纪50年代平均每年9.55 Gg增加到了90年代每年32.26 Gg, 同期伴随着水稻单产的增加. 在20世纪50～90年代间, 我国水稻生产的N₂O-N排放量以平均每10 a6.74 Gg的速度递增. 20世纪50年代和90年代稻田N₂O-N季节排放通量平均分别为0.32 kg·hm^-2和1.00 kg·hm^-2, 相当于季节氮输入总量的0.37%和0.46%. 本研究模型估算50～90年代间稻田N₂O季节排放量的不确定性为59.8%～37.5%. 就全国稻田的不同种植区域而言, 长江中下游地区稻田水稻生长季N₂O排放量占全国稻田N₂O排放总量的51%～56%. 20世纪90年代水稻生长季N₂O排放量约占我国农田N₂O年总排放量的8%～11%. 相对于旱地作物而言, 过去几十年水稻生产的发展在很大程度上减缓了我国农业生产的N₂O排放. 然而, 随着水稻生产中节水灌溉的推广和氮肥施用量的增加, 我国稻田N₂O季节排放量预计将相应增加.     

DNDC模型在长江三角洲农田生态系统的CH4和N2O排放量估算中的应用

长江三角洲是我国农业发达地区之一,其农业生产所排放的CH₄和N₂O,早已引起了研究者的重视.本研究在分析总结现有的野外观测结果的基础上,验证了估算区域痕量气体排放量的生物地球化学模型DNDC,估算出长江三角洲地区的CH₄和N₂O排放量分别为1.69(1.29～2.09)Tg·a^-1和0.019(0.014～0.024)Tg·a^-1,分别占全国农田CH₄和N₂O排放量的16.7%和6.1%.