外源氮添加对湿地土壤N_2O排放量的影响

为搞清湿地土壤驱动N2O排放的关键氮源类型,有效减少湿地N2O的排放,本文通过室内控制温湿度,用气相色谱法分析不同外源氮素对湿地N2O排放的影响。结果表明:外加氮源组总是高于对照组N2O排放量(4.4 mg·m-3)。在设定的剂量范围内,单独添加尿素或尿素与硝酸铵1∶1配合时N2O排放量呈现先增后减的单峰分布趋势,峰值分别为10.6 mg·m-3和229.0 mg·m-3;单独添加硝酸铵时N2O排放量(32.6~111.0 mg·m-3)随着氮素添加量增加呈现持续上升趋势。单独添加尿素或硝酸铵、尿素与硝酸铵1∶1配合均促进N2O的排放,但硝酸铵尿素混合添加对N2O排放量的贡献单独添加硝酸铵单独添加尿素。这为预测内蒙古高原区农牧交错带湿地氮素输入可能带来的温室效应和有效减排提供科学依据。     

The Effect of N Deposition on Nitrous Oxide and Nitric Oxide Emissions from Temperate Forest Soils

Long-term and short-term N deposition effects on N₂O and NO emissions from forest soils were compared. Long-term NH₃ deposition (> 20 years) from a poultry farm to a downwind woodland (decreasing from 73 to 18 kg N ha^-1 y^-1, 30 to 110 m downwind of the farm) resulted in the re-emission of 6% and 14% of NH₃-N deposited as N₂O-N and NO-N, respectively. However, when in short-term (2-3 years) field experiments the atmospheric N deposition to mature conifer plantations was raised by fumigation with NH₃ to 15 kg N ha^-1 y^-1 or by acid mist to 48 and 96 kg N ha^-1 y^-1 the N deposited was immobilised. In the acid mist experiment more than 2 years of acid mist (48 and 96 kg N ha-1 y^-1) were required to significantly increase N₂O emissions from -0.3 μg N₂O-N m^-2 h^-1 (control) to 0.5 and 5.7 μg N₂O-N m^-2 h^-1, respectively. This suggests, that N deposition simulation studies in soil ecosystems, which have previously not been exposed to high rates of N (by deposition or fertilisation), need to be long-term. Also, measurements of N₂O and/or NO may be a non-destructive, quick indicator of the N status of the soil.     

农田土壤中N_2O释放的水温特征研究

室内模拟研究不同水热条件下土壤中N2O的释放特征,有助于阐明N2O释放的水热效应机理。本文通过室内试验研究了西北地区的典型耕种土壤土娄土中N2O在不同水温变化下的释放特征,借助化学反应动力学理论对其释放机理进行了初步的探讨。结果表明:10℃和30℃下,不同含水量的土壤中N2O的浓度变化随着培养时间的延长呈"S"型曲线。可用方程C=1/[A+Bexp(-t)]来描述。随着温度的升高(10℃到30℃),N2O释放的快速期,减速期,稳定期的启动时间明显提前。在较低的土壤湿度范围内(27%至58%wfps),土壤中N2O释放的稳定浓度与土壤湿度呈正相关;田间持水量(58%wfps)时,N2O释放的稳定浓度达到最大;超过田间持水量时,其逐渐变小。当土壤湿度从27%-42%wfps增加时,30℃下土壤中N2O释放的稳定浓度大于10℃下的;当土壤湿度等于或大于田间持水量(58%wfps)时,30℃下土壤中N2O释放的稳定浓度小于10℃下的。低温下(10℃)的风干土壤(8%wfps)存在吸收N2O的现象。不同水热条件下土壤硝化和反硝化过程中N2O释放的表观化学反应速率常数和对应活化能的大小决定了土壤中N2O的释放量及难易程度。     

有机无机肥料配施对春玉米农田N2O排放及净温室效应的影响

为了明确有机无机肥料配施条件下华北旱地春玉米农田N2O周年排放规律、影响因素及其净温室效应,采用静态箱-气相色谱法和生物地球化学模型（DNDC）相结合的方法,对单施化肥（NPK）、有机无机肥料配施（50％M＋50％U）、单施有机肥（M）、对照（CK）等处理的春玉米农田N2O排放情况进行了周年监测,并对DNDC模型进行验证,利用验证后的模型定量评价了不同施肥处理的净温室效应。结果表明：不同有机无机肥料配施处理N2O放通量具有明显的季节变化规律,通量变化范围是-17．56—157．25μg·m2·h-1,在非生长季观测到明显的N2O排放峰,最大排放通量为83．85μg·m2·h-1。NPK、50％M＋50％U、M、CK处理周年累计排放量分别为1．49、1．20、0．82、0．61kgN·hm-2·a-1,非生长季排放总量分别占全年总排放量的40．6％、59．2％、61．7％和60．7％,非生长季N2O排放不容忽视;在整个周年观测期内,当土壤水分含量介于19％-37％之间时,各处理下的N2O通量同土壤含水量呈极显著正相关关系。综合考虑整个农田生态系统碳收支平衡和温室气体排放,经过DNDC模型模拟表明有机无机肥料配施同单施化肥处理相比净温室效应减少33．5％,可以达到在保持产量的基础上“减排”和“固碳”的协同效果。上述研究结果为有机无机肥料合理使用以及旱地农田“稳产、减排、固碳”相协调施肥技术的筛选提供了科学依据。     

冬小麦/大葱轮作体系N_2O排放特征及影响因素研究

采用静态暗箱-气相色谱法研究了冬小麦/大葱轮作体系不同施肥处理下农田N2O排放特征及排放系数,分析了土壤湿度和土壤温度等环境因子对N2O排放的影响。结果表明,农田N2O排放高峰值主要出现在每次施肥＋灌溉或强降雨之后的一段时间,大葱生长季排放峰值高且出现的频率比小麦生长季密集;N2O排放通量变化范围为-3.85～507.11μg N·m-2·h-1,平均值为251.63μgN·m-2·h-1,对于不同施肥处理,其年度N2O排放总量介于1.71 kg N·hm-2到4.60 kg N·hm-2之间。整个轮作体系不同处理N2O排放系数介于0.31%到0.48%之间,均值为0.43%;相对比农民习惯（FP）处理,优化施肥（OPT）、优化减氮（OPT-N）以及秸秆还田（C/N）处理均能显著减少N2O的排放,秸秆还田处理和优化减氮处理N2O排放总量比优化处理分别减少了17%和10%。在10℃〈土壤温度（T）s〈20℃时,N2O排放随温度的升高而增加;整个小麦生长季N2O排放随土壤湿度的增加而增加,且达到0.05的显著水平;大葱生长季在20℃〈Ts〈30℃时,土壤水分含量成为主要限制因素,N2O排放与土壤孔隙含水量（WFPS）呈显著指数正相关关系。秸秆还田处理作物产量高于其他处理,是具有减排增产＂双赢＂效果的农田管理措施。     

不同氮磷肥施用对春玉米农田N_2O排放的影响

农田过量施肥会增加N2O排放,使农田土壤成为重要的温室气体排放源。为减少农田N2O排放,利用自动观测系统研究了春玉米农田中不同肥料对N2O排放的影响,并结合作物产量及N2O的排放量探索减少温室气体排放的施肥措施。采用田间试验方法设定了不施肥（CK）、尿素（U）、尿素加磷肥（NP）和硝酸磷肥（NOP）4个处理进行研究。结果表明,各处理下N2O排放总量分别为：CK0.21kgN·hm-2、U1.19kgN·hm-2、NP0.93kgN·hm-2、NOP0.69kgN·hm-2;N2O排放主要受施肥、灌溉,降雨和土壤温度的影响;在作物生长后期土壤含氮量小于7mgN·kg-1的情况下,观测到土壤吸收N2O的情况;各处理下排放因子均小于政府间气候变化委员会（IPCC）的缺省值1%,表明IPCC推荐的排放因子不适用于估算中国北方的春玉米农田N2O排放。施加磷肥有助于减少农田N2O排放并提高产量,硝态磷肥较尿素可以显著减少N2O排放。综合考虑产量和N2O排放,相对于施用尿素和尿素加磷肥处理,硝酸磷肥处理不仅可节约15%和30%的肥料投入,而且分别减少42%和26%的N2O排放,具有减排不减产的良好效果。     

Influence of Watering Methods on the Short-Term Pulse Emissions of Nitrous Oxide from Disturbed Horticultural Soil

To reveal the impact of soil disturbance and surface watering (SW) following soil disturbance on the pulse nitrous oxide (N₂O) emissions, incubated experiments were conducted on disturbed soil with two watering regimes [surface watering only (SWO) and subsurface watering followed by surface watering (SUW+SW)]. Intensive soil disturbance led to pulses N₂O emissions from SUW + SW soil (>8,693 μg N₂O m^?2 h^?1 with a peak of 30,938 μg N₂O m^?2 h^?1), although the water-filled pore space (WFPS) was substantially lower than the previously reported optimal soil moisture range (45–75% WFPS) for peak N₂O emissions. N₂O emissions from the disturbed soil after SW were much lower than those from SUW + SW soil, increased as the soil dried, and peaked when the WFPS fell within the optimal soil moisture range. These peaks were considerably less than those resulting from the intensive disturbance in SUW + SW soil. Thus, SW after intensive soil disturbance may be effective for mitigating of pulse N₂O emissions caused by soil disturbance.     

Emissions of trace gases (CO2, CO,CH4, and N2O) resulting from rice straw burning

Emissions of trace gases (CO₂, CO, CH₄, N₂O) resulting from rice straw burning were measured by using the open chamber method. The carbon contained in rice straw was mainly released to the atmosphere as CO₂. The percentage of CO₂-C emitted in total C in rice straw was in the range of 57–81%, followed by CO-C (5–9%). The percentages of CH₄-C and N₂O-N in total C and N in rice straw were in the range of 0.43–0.90 and 1.16–1.50%, respectively. In the case of the rice straw which had been left in the field for a period of one month after harvest, emission of imperfect combustible gases such as CO and CH₄ during burning increased slightly, while that of perfect combustible gas, CO₂, was reduced. The amount of CH₄ emission from rice straw burning was comparable to that from paddy fields.     

Nitrous Oxide Emissions from Newly Created Littoral Marshes in the Drawdown Area of the Three Gorges Reservoir, China

This study aimed to understand the seasonal and spatial variations of N₂O emissions from newly created littoral marshes in the drawdown area of the Three Gorges Reservoir (TGR), China. We measured N₂O emissions at 10-day intervals during the growing season (early July to late September) in 2008. N₂O emissions were measured with static chambers in four typical vegetation stands. The results showed great spatial variations of N₂O emissions among the four stands. The greatest N₂O emissions (0.052?±?0.063 mg N₂O m^?2?h^?1) were from Scirpus triqueter stand, while the lowest N₂O emissions (0.020?±?0.020 mg N₂O m^?2?h^?1) were from Typha angustifolia stand. To such spatial variations in N₂O emissions, standing water depths and soil water content may be important explaining factors. Besides spatial variations, we also found significant temporal variations of N₂O emissions in this area. The temporal variation of N₂O emissions in the growing season was not found significantly related to any measured factor in the study. However, based on principal component analysis, we consider it partly caused by thermal conditions and the marked temporal variation of the standing water depth in the growing season, which to some degree influenced the process of denitrification and N₂O emissions. These results about TGR enable us to make a more reasonable estimate of N₂O emissions from large dam reservoirs, particularly those with a large drawdown area in the growing season in an agricultural landscape.     

长期秸秆还田对设施菜田土壤反硝化特征和N2O排放的影响

基于2004年2月-2010年9月温室菜田长期定位试验,通过室内培养和田间同步,利用静态箱法和硅胶管法分别检测土壤表层N2O通量和剖面N2O浓度的变化,以研究高碳氮比的小麦秸秆施用对设施菜田土壤反硝化过程及N2O排放的影响.结果表明,（1）与对照处理（CK）相比,添加秸秆处理（ST）显著提高0-20cm土层土壤反硝化量,促进N2O还原,增加N2产生量,显著降低追肥灌溉后表层土壤N2O的排放峰值和土壤底层50cm处N2O浓度峰值,但对20-80cm土层土壤的反硝化特征影响较少.（2）秸秆还田有利于降低设施菜田NO;淋洗风险,秸秆的深施是进一步降低菜田NO3-淋洗的有效途径,有利于土壤底层N2O的再次还原.因此,设施菜田中添加小麦秸秆并深施有利于降低N2O排放和减少NO3-的淋洗.     

黄土丘陵区不同土地利用类型土壤CO_2,N_2O通量特征

以黄土丘陵区园则沟小流域农地、撂荒草地、红枣林3种土地利用类型为单元,采用静态箱—气象色谱法对生长季土壤CO_2,N_2O两种温室气体进行定位监测,研究退耕还林(草)工程实施后不同土地利用类型土壤CO_2,N_2O排放通量特征。结果表明:生长季农地、撂荒草地、红枣林土壤CO_2排放通量均值分别为300.39,273.31,173.80mg/(m~2·h),季节变化均呈单峰型;农地、撂荒草地、红枣林N_2O通量均值分别为7.08,9.26,0.52μg/(m~2·h),土地利用类型未明显改变N_2O通量的季节特征,各处理均于6—7月出现较大值,其他时期均较低或出现负排放并呈现较为复杂的源汇特征。土壤10cm温度与土壤CO_2,N_2O相关关系高于土壤水分,而3种土地利用类型下N_2O通量与土壤水分均不相关,二元线性回归结果显示水热双因子解释了54%~78%的土壤CO_2通量变异。综合分析表明黄土丘陵区退耕还草后土壤CO_2未有显著变化,土壤N_2O则随土壤基质条件的改善呈现上升趋势(p0.01);坡耕地改为经济林后土壤CO_2,N_2O通量均有一定程度减少(42.1%~92.7%),且更容易出现N_2O的负排放。     

Emissions of Greenhouse Gases CH4 and N2O from Low-gradient Streams in Agriculturally Developed Catchments

Lentic wetlands are usually regarded as the most important natural freshwater sources of methane (CH₄) and nitrous oxide (N₂O) to the atmosphere, and very few studies have quantified the importance of lowland streams in trace gas emissions. In this study, we estimated fluxes of CH₄ and N₂O in three macrophyte-rich, lowland agricultural streams in New Zealand, to place their trace gas emissions in context with other sources and investigate the value of minimising their emissions from agricultural land. All three streams were net sources of both gases, with emission of CH₄ ranging from <1 to 500 μmol m^?2 h^?1 and of N₂O ranging from <1 to 100 μmol m^?2 h^?1 during mid-summer. For CH₄, both turbulent diffusion across the surface and ebullition of sediment gas bubbles were important transport processes, with ebullition accounting for 20–60% of the emissions at different sites. The emissions were similar on a per area basis to other major global sources of CH₄ and N₂O. Although small on a catchment scale compared to emissions from intensively grazed pastures, they were significant relative to low-intensity pastures and other agricultural land uses. Because hydraulic variables (viz. depth, velocity and slope) strongly influence turbulent diffusion, complete denitrification can best proceed to N₂ as the dominant end-product (rather than N₂O) in riparian wetlands, rather than in open stream channels where N₂O fluxes are sometimes very large.     

水肥减量对设施芹菜地N2O排放的影响

为明确减量灌溉和施肥对设施菜地N₂O排放的影响,提出有效的N2O减排措施,本研究采用静态箱法,对北京郊区设施芹菜在灌溉和有机肥（沼渣）减量处理下的N₂O排放进行全生长季监测,分析灌溉和有机肥减量对土壤充水孔隙度（WFPS）、NO₃--N和NH₄+-N含量及土壤N2O排放的影响。试验为2个灌溉量和3个有机肥施用量的裂区双因素设计,具体为：常规灌溉量（H处理）下的常规施肥(HN)、减量1/3施肥(HN₃)和不施肥 (HN0),以及减量20%灌溉（L处理）下的常规施肥(LN)、减量1/3施肥(LN3)和不施肥 (LN0)共6个处理。结果表明,L处理在保证芹菜产量的前提下,对土壤充水孔隙度及无机氮含量无显著影响,但N₂O排放总量较H处理减少32.23%,达极显著水平（P＜0.01）。与常规施肥处理相比,减量1/3施肥和不施肥处理的土壤NO₃--N含量分别降低43.96%和76.42%,均达极显著水平（P＜0.01）,不同施肥量处理间土壤NH₄+-N含量无显著差异;芹菜产量随施氮量增加而增加,但减量1/3施肥和常规施肥处理对芹菜产量影响无显著差异,芹菜全生长季的土壤累积N₂O排放总量显著减少62.04%（P＜0.01）。本试验条件下,减量20%灌溉（L处理）和减量1/3施肥（N3处理）均能保证芹菜产量,显著降低芹菜地N2O排放通量,减少生产成本投入。     

外加可溶性碳源对华北典型农田土壤N2O、CO2排放的影响

以华北平原典型农田土壤为对象,运用静态培养系统研究方法,设置室内培养试验,研究添加不同浓度葡萄糖对土壤N2O、CO2排放的影响.结果表明:碳氮配施的外源添加方式明显促进N2O和CO2排放,其排放通量均高于对照组和只添加氮源的处理.在配施碳源葡萄糖浓度为0.5 g/kg时N2O排放通量最高(NH4+组2 500 μg/(kg·d),单位以N计,下同,NO3-组1 500 μg/(kg·d)),4.0 g/kg时N2O排放通量最低(NH4+组500 μg/(kg·d),NO3-组800 μg/(kg·d));葡萄糖浓度为2.0 g/kg时CO2排放通量最高(NH+组500mg/(kg· d)),0.5 g/kg时CO2排放通量最低(NH+组100 mg/(kg,d)).从培养开始到结束,只添加氮源的土壤NH+含量变化不明显,NO3-含量增至29.21 mg/kg(NH4+组)和62.25 mg/kg(NO3-组);而配施葡萄糖的土壤NH+含量降为不足1 mg/kg(NH4+组),NO3-含量明显减少.N2O累积排放通量与葡萄糖浓度呈负相关(NH4+组),CO2累积排放通量与葡萄糖浓度呈正相关.分析结果表明,外加可溶性碳源明显减少土壤中NH4+和NO3-含量,并且促进土壤N2O、CO2排放,其排放通量大小与C/N比有关.     

添加生物炭对华南早稻田CH4和N2O排放的影响

通过田间试验,采用静态箱-气象色谱法研究生物炭添加对华南早稻田甲烷(CH4)和氧化亚氮(N2O)排放的影响.试验设对照(CK),BC1、BC2、BC3(土壤中分别混入5、10、20t·hm-2生物炭)、RS(稻草直接还田)和RI(稻草加腐熟剂还田)6个处理.结果表明,与CK、RS和RI相比,生物炭处理能降低稻田CH4和N2O排放量及排放强度,综合排放强度最低的为BC3处理,值为0.98 kgCO2-eq· kg-1.在本实验的处理范围内,生物炭添加量越高,CH4平均排放通量及其季节排放总量越低,最低值分别为22.11mg·m-2·h-1和93.21kg·hm-2;N2O排放通量和季节排放总量则随生物炭添加量的增加呈上升趋势,最高值分别为285.65 μg·m-2·h-1和1.07kg·hm-2,但依然小于对照处理(368.13μg·m-2 ·h-1和1.13kg·hm-2).此外,试验发现高用量的生物炭(即BC3)处理水稻产量最高,值为7152.58kg·hm-2.综合分析各处理,BC3对减缓温室效应和稳定水稻生产贡献最大.     

铵态氮源和碳源对土壤N_2O、CO_2释放的影响

在田间持水量WFPS为70%、温度为20℃的条件下,通过室内静态培养方法研究铵态氮源与不同碳源结合,对华北平原典型小麦-玉米轮作体系土壤N_2O、CO_2释放的影响。其中,碳源种类分别为葡萄糖、果胶、淀粉、纤维素、木质素和秸秆。结果表明添加葡萄糖和果胶有效促进了土壤N_2O的释放,并在第1 d达到最大值,分别为4 039.85μg N_2O-N·kg~(-1)·d~(-1)和2 533.44μg N_2O-N·kg~(-1)·d~(-1);添加纤维素和只施秸秆处理降低了N_2O释放。施入碳源增加了CO_2释放,顺序为纤维素淀粉葡萄糖果胶秸秆木质素。培养结束后土壤中铵态氮几乎消耗完全,除添加葡萄糖处理外,其他施碳土壤的硝态氮含量均有所增加。在培养前3d,土壤NH~+_4和NO~-_3总含量与N_2O释放量显著相关。     

Emissions of CH4, CO2, and N2O from soil at a cattle overwintering area as affected by available C and N

Relationships between CH₄, CO₂, and N₂O emissions were studied in soil that had been freshly amended with large deposits of cattle wastes. Dynamics of CH₄, CO₂, and N₂O emissions were investigated with flux chambers from early April to late June 2011, during the 3 months following cattle overwintering at the site. This 81-day field study was supplemented with soil analyses of available C and N content and measurement of denitrification activity. In a more detailed field investigation, the daily time course of emissions was determined. The field research was complemented with a laboratory experiment that focused on the short-term time course of N₂O and CH₄ production in artificially created anoxic soil microsites. The following hypotheses were tested: (i) a large input of C (and N and other nutrients) in cattle manure creates conditions suitable for methanogenesis, and therefore overwintering areas can produce large amounts of CH₄; (ii) N₂O is produced and emitted until the level of mineral N decreases, while the level of CH₄ production is low; and (iii) production of CH₄ is greater when N immobilization decreases the level of NO₃⁻ in soil. N₂O emissions were relatively large during the first 3 weeks, then peaked (at ca. 4000 μg N₂ON m⁻² h⁻¹) and soon decreased to almost zero; the changes were related to the mineral and soluble organic N content in soil. CH₄ fluxes were large, though variable, in the first 2 months (600–3000 μg CH₄C m⁻² h⁻¹) and were independent of C and N availability. Although time courses differed for CH₄ and N₂O, a negative relationship between N₂O and CH₄ emissions was not detected. Contrary to CH₄ and N₂O fluxes, CO₂ emissions progressively increased to ca. 300 mg CO₂C m⁻² h⁻¹ at the end of the field study and were closely related to air and soil temperatures. Diurnal measurements revealed significant correlations between temperature and emissions of CH₄, N₂O, and CO₂. Addition of C to soil during anaerobic incubation increased the production and consumption of N₂O and supported the emission of CH₄. The results suggest that rapid denitrification significantly contributes to the exhaustion of oxidizing agents and helps create microsites supporting methanogenesis in otherwise N₂O-producing upland soil. The results also indicate that accurate estimate of gas fluxes in animal-impacted grassland areas requires assessment of both diurnal and long-term changes in CH₄, CO₂, and N₂O emissions.     

N2O,NO, and NH3 Emissions from Soil after the Application of Organic Fertilizers,Urea and Water

Water, Air, & Soil Pollution - Agricultural soil is a major source of nitrous oxide (N2O), nitric oxide (NO) and ammonia (NH3). Little information is available on emissions of these gases from...     

N2O, NO, and NH3 Emissions from Soil after the Application of Organic Fertilizers, Urea and Water

Agricultural soil is a major source of nitrous oxide (N₂O), nitric oxide (NO) and ammonia (NH₃). Little information is available on emissions of these gases from soils amended with organic fertilizers at different soil water contents. N₂O, NO and NH₃ emissions were measured in large-scale incubations of a fresh sandy loam soil and amended with four organic fertilizers, [poultry litter (PL), composted plant residues (CP), sewage sludge pellets (SP) and cattle farm yard manure (CM)], urea fertilizer (UA) or a zero-N control (ZR) for 38 days. Fertilizers were added to soil at 40, 60 or 80% water-filled pore space (WFPS). The results showed that urea and organic fertilizer were important sources of N₂O and NO. Total N₂O and NO emissions from UA ranged from 0.04 to 0.62%, and 0.23 to 1.55% of applied N, respectively. Total N₂O and NO emissions from organic fertilizer treatments ranged from 0.01 to 1.65%, and <0.01 to=" 0.55%=" of=" applied=" n,=" respectively.=" the=" lower=">₂O and NO emissions from CP and CM suggested that applying N is these forms could be a useful mitigation option. Comparison of the NO-N/N₂O-N ratio suggested that nitrification was more dominant in UA whereas denitrification was more dominant in the organic fertilizer treatments. Most N was lost from PL and UA as NH₃, and this was not influenced significantly by WFPS. Emissions of NH₃ from UA and PL ranged from 62.4 to 69.6%, and 3.17 to 6.11% of applied N, respectively.