不同种类氮肥对土壤释放N2O的影响

用培养试验模拟研究了在正常水分(22%)、干旱(12%)和高含水量(32%)条件下,普通碳酸氢铵(普碳)、尿素及新型肥料长效碳酸氢铵(长碳)对土壤释放N₂O的影响;同时考察了土壤NO₃^-的形成时间和形成量.结果表明,农田中施加的无机氮肥是大气中N₂O的重要来源,而长碳与普碳和尿素相比,不但可以明显延后N₂O释放高峰期出现时间,而且大多数情况下可以显著减少其释放量(P<0.01).在5个月的监测期内,与普碳和尿素相比其减少N₂O释放的比例分别为80.23和88.41%(12%含水量),40.00和27.59%(22%含水量),无减少作用和45.88%(32%含水量).本研究结果提示长碳具有作为农田生态系统N₂O减排措施的巨大潜力,同时暗示在农业中用长碳代替目前普遍应用的普碳,可以减少地下水中NO₃^-引起的污染.     

长效碳酸氢铵对土壤硝化-反硝化过程和NO与N2O排放的影响

室内实验(25℃和50%WFPS)比较研究了碳酸氢铵(普碳)和长效碳酸氢铵(长碳)对粘质土壤(粘土)和壤质土壤(壤土)硝化反硝化过程和NO与N2O排放的影响.长碳中的DCD在粘土中的硝化抑制作用很弱,在壤土中显著,与普碳处理相比,NH 4持续时间分别延长7d和33d.15d内,施普碳(100μgN·g-1)情况下,粘土和壤土NO排放量分别占施N量的060%和106%,分别是相应土壤N2O排放量的30和12倍.施长碳后,粘土和壤土NO排放量分别减少67%和95%,N2O排放量分别减少64%和55%.有氧培养39d后,外加硝酸盐(200μgKNO3N·g-1),接着淹水厌氧培养7d,壤土长碳处理较普碳处理反硝化总损失减少50%,但N2O排放量增加113%.     

长效碳酸氢铵对土壤硝化-反硝化过程和NO与N2O排放的影响

室内实验(25℃和50%WFPS)比较研究了碳酸氢铵(普碳)和长效碳酸氢铵(长碳)对粘质土壤(粘土)和壤质土壤(壤土)硝化反硝化过程和NO与N₂O排放的影响.长碳中的DCD在粘土中的硝化抑制作用很弱,在壤土中显著,与普碳处理相比,NH₄⁺持续时间分别延长7d和33d.15d内,施普碳(100μgN·g^-1)情况下,粘土和壤土NO排放量分别占施N量的0.60%和1.06%,分别是相应土壤N₂O排放量的30和12倍.施长碳后,粘土和壤土NO排放量分别减少67%和95%,N₂O排放量分别减少64%和55%.有氧培养39d后,外加硝酸盐(200μgKNO₃-N·g^-1),接着淹水厌氧培养7d,壤土长碳处理较普碳处理反硝化总损失减少50%,但N₂O排放量增加113%.     

长效氮肥施用对黑土水旱田CH4和N2O排放的影响

通过在黑土玉米地与水稻田施用长效氮肥后发现 ,长效碳酸氢铵 (长碳 )与长效尿素(长尿 )能显著减少黑土玉米地N2 O的排放。与施用普通尿素相比 ,其排放量分别减少了5 9 2 %和 73 3%。长碳和长尿还能促进黑土玉米地对CH4的吸收作用。黑土水稻田施用长尿后 ,N2 O的排放减少了 6 1%。而CH4的排放却略有增加     

干湿交替频率对不同土壤CO2和N2O释放的影响

干旱、半干旱和地中海气候区,乃至一些湿润地区,由干湿交替引起的土壤碳、氮的短暂脉冲式释放很大程度上决定着长时间尺度温室气体释放的总量,是土壤碳、氮温室气体释放的关键过程.选择我国降雨梯度下的森林、农田、草地和荒漠生态系统,采集土样进行实验室统一控制条件下的多重干湿交替循环,对比探讨不同生态系统土壤干湿交替频率对CO2和N2O释放的影响模式.结果表明:(1)干湿交替能够显著的激发土壤中CO2和N2O的释放,森林、农田、草地和荒漠土壤CO2和N2O释放速率对干湿交替的响应模式基本一致,其响应强度与土壤本底中碳和氮的含量有关;(2)在一定培养时间内,随着干湿交替频率的增加,土壤再湿润阶段CO2释放速率降低,但是,气体释放的总量较之于恒湿对照组有所增加.(3)不同土壤N2O的释放总量对于湿交替频率的响应模式表现出很大的差异,其中农田和荒漠土壤响应模式类似.     

氮肥调控剂对潮褐土中不同氮源氮素转化及油菜生长的影响

采用土壤培养和盆栽试验相结合的方法,研究了硝化抑制剂双氰胺(DCD)与纳米碳配合施用对尿素和碳酸氢铵在华北平原典型土壤潮褐土中转化的调控效果及其对油菜生长的影响.结果表明： 尿素和碳酸氢铵在施入土壤后的2周内,土壤无机氮的供应强度差别较大,2周以后则基本相似.2种氮源对油菜生长及氮素利用的影响在生育前期(播种后34 d)差异显著,但最终达到商品生物量收获时,氮源之间差异不大.DCD对尿素和碳酸氢铵在潮褐土中的转化表现出显著的硝化抑制作用,其抑制强度和有效抑制时间随DCD用量的增加而增强,且以对碳酸氢铵施入土壤后的硝化抑制效果更好.在本研究条件下,DCD用量以占肥料纯氮量的1.0%～1.5%相对较佳,可显著提高油菜产量,改善叶色,降低植株硝酸盐含量,提高氮肥利用率.纳米碳与DCD配合施用对土壤铵氧化有明显的协同抑制效果,且可以显著刺激油菜前期的生长发育和氮素利用,降低油菜硝酸盐含量.     

氮肥调控剂对潮褐土中不同氮源氮素转化及油菜生长的影响

采用土壤培养和盆栽试验相结合的方法,研究了硝化抑制剂双氰胺(DCD)与纳米碳配合施用对尿素和碳酸氢铵在华北平原典型土壤潮褐土中转化的调控效果及其对油菜生长的影响.结果表明:尿素和碳酸氢铵在施入土壤后的2周内,土壤无机氮的供应强度差别较大,2周以后则基本相似.2种氮源对油菜生长及氮素利用的影响在生育前期(播种后34 d)差异显著,但最终达到商品生物量收获时,氮源之间差异不大.DCD对尿素和碳酸氢铵在潮褐土中的转化表现出显著的硝化抑制作用,其抑制强度和有效抑制时间随DCD用量的增加而增强,且以对碳酸氢铵施入土壤后的硝化抑制效果更好.在本研究条件下,DCD用量以占肥料纯氮量的1.0％ ～1.5％相对较佳,可显著提高油菜产量,改善叶色,降低植株硝酸盐含量,提高氮肥利用率.纳米碳与DCD配合施用对土壤铵氧化有明显的协同抑制效果,且可以显著刺激油菜前期的生长发育和氮素利用,降低油菜硝酸盐含量.     

控释肥及其与尿素配合施用对水稻生长期N_2O排放的影响

通过田间试验,采用静态箱法研究相同施氮量条件下,施用尿素、控释肥及尿素与控释肥配施(尿素与控释肥以3:7配合施用)对稻田N2O排放的影响.结果表明:与单施尿素处理相比,配施处理和控释肥处理水稻生长期N2O排放量分别减少40.4%和59.6%(P<0.05),其中烤田期分别减少65.1%和83.9%;与配施处理相比,施用控释肥处理N2O排放量略微减少(P>0.05),其中烤田期减少53.9%.施用控释肥可增加水稻产量,与尿素处理相比,施用控释肥和配施处理水稻产量分别增加7.8%和9.8%(P>0.05).施用控释肥使土壤无机氮峰值出现时间延后,烤田期N2O排放减少.水稻生长期N2O排放通量与土壤氧化还原电位(Eh)和土壤温度均无明显相关性(P>0.05).     

长效碳酸氢铵缓效机理与环境效应研究

依据长效碳铵的光谱特征、理化特性及其对影响氨挥发的主要因子的分析 ,建立了土壤中氨挥发的数学模式 ,提出了长效碳铵中DCD与从碳铵中离解出来的游离态氨形成分子间氢键的新观点 ,这种弱相互作用力降低了土壤中氨的表观浓度 ,使土壤 pH在氨挥发期间降低了 0 .2～ 0 .4,延缓了NO-3 N形成时间 ,缓解了N损失 .长效碳铵能够调节N素供应的形态、时间与数量 ,减少施用化肥后引起的地面水和地下水硝酸盐的污染 .     

保护性耕作对农田生态系统净碳释放量的影响

以华北平原小麦-玉米两熟地区保护性耕作5年田间定位试验为基础,利用West提出的净碳释放方程对翻耕、少耕和免耕3种耕作方式下农田各项投入造成的碳释放和土壤碳累积进行比较。结果表明:在翻耕、少耕、免耕3个处理下,5年间各项农田投入造成的碳释放分别为312.60、295.4和280.52kg.km-2.a-1,表层30cm土壤的碳储量分别为30.59、32.76和31.61Mg.km-2,农田净碳释放量分别为312.60、-138.59和-76.52kg.km-2.a-1;与翻耕地比较,免耕和少耕地的相对净碳释放量为-236.08和-451.19kg.km-2.a-1;免耕地农田投入的碳减排量(32.08kg.km-2.a-1)为土壤碳增汇量(204.00kg.km-2.a-1)的15.73%,少耕地农田投入的碳减排量(17.19kg.km-2.a-1)为土壤碳增汇量(434.00kg.km-2.a-1)的3.96%。少耕地对减少大气CO2的贡献大于免耕地。     

长效碳酸氢铵对土壤硝化-反硝化过程和NO与N2O排放的影响

Compared with ammonium bicarbonate(AB), the effect of modified ammonium bicarbonate (MAB) on nitrification and denitrification processes and NO and N2O emissions in a clay soil (C soil) and a loam soil (L soil) was studied in laboratory (25 degrees C and 50% WFPS). The inhibition effect of DCD from MAB on nitrification was relatively small in C soil, but considerably great in L soil. Compared with AB, MAB extended 7 days and 33 days for retaining NH4+. During 15 days, the NO emission from C soil and L soil respectively accounted for 0.60% and 1.06% of applied N under AB application (100 micrograms N.g-1), which were as 30 and 12 times as the N2O emission from corresponding soils. After applying MAB, the emission of NO from C soil and L soil decreased by 67% and 95%, and the emission of N2O decreased by 64% and 95%, respectively. After 39 days of aerobic incubation, then anaerobically flooded incubation with nitrate addition (200 micrograms KNO3-N.g-1) for 7 days, the total loss of denitrification in MAB in L soil was 50% less, and N2O emission was 113% more than in AB in same soil.     

南京市郊区集约化大棚蔬菜地N2O的排放

采用静态暗箱-气相色谱法,研究了南京市郊区集约化生产管理下,芹菜-空心菜-小白菜-苋菜轮作菜地与休闲裸地的N2O排放通量的动态变化,及其与土壤温度、湿度以及NO3--N和NH4+-N含量的关系.结果表明:轮作菜地的N2O累积排放量达137.2kg N·hm-2,显著大于休闲裸地(29.2 kgN-hm-2);轮作菜地生态系统N2O-N的排放系数高达4.6％.4种蔬菜地中,空心菜地对轮作菜地的周年累积排放量贡献最大,为53.5％,小白菜地次之,为31.9％,芹菜地和苋菜地最小,分别为4.5％和4.8％.轮作菜地的N2O排放通量与土壤温度呈显著正相关,Q10为2.80;土壤湿度以及NO3--N和NH4+-N含量与轮作菜地的N2O排放通量之间的相关性不显著.     

Short-term nitrous oxide emissions from pasture soil as influenced by urea level and soil nitrate

Nitrogen excreted by cattle during grazing is a significant source of atmospheric nitrous oxide (N₂O). The regulation of N₂O emissions is not well understood, but may vary with urine composition and soil conditions. This laboratory study was undertaken to describe short-term effects on N₂O emissions and soil conditions, including microbial dynamics, of urea amendment at two different rates (22 and 43 g N m⁻²). The lower urea concentration was also combined with an elevated soil NO ₃ ⁻ concentration. Urea solutions labelled with 25 atom%¹⁵N were added to the surface of repacked pasture soil cores and incubated for 1, 3, 6 or 9 days under constant conditions (60% WFPS, 14 °C). Soil inorganic N (NH ₄ ⁺ , NO ₂ ⁻ and NO ₃ ⁻ ), pH, electrical conductivity and dissolved organic C were quantified. Microbial dynamics were followed by measurements of CO₂ evolution, by analyses of membrane lipid (PLFA) composition, and by measurement of potential ammonium oxidation and denitrifying enzyme activity. The total recovery of¹⁵N averaged 84%. Conversion of urea-N to NO ₃ ⁻ was evident, but nitrification was delayed at the highest urea concentration and was accompanied by an accumulation of NO ₂ ⁻ . Nitrous oxide emissions were also delayed at the highest urea amendment level, but accelerated towards the end of the study. The pH interacted with NH ₄ ⁺ to produce inhibitory concentrations of NH₃(aq) at the highest urea concentration, and there was evidence for transient negative effects of urea amendment on both nitrifying and denitrifying bacteria in this treatment. However, PLFA dynamics indicated that initial inhibitory effects were replaced by increased microbial activity and net growth. It is concluded that urea-N level has qualitative, as well as quantitative effects on soil N transformations in urine patches.     

Contributions of Autotrophic and Heterotrophic Nitrifiers to Soil NO and N(2)O Emissions

Soil emission of gaseous N oxides during nitrification of ammonium represents loss of an available plant nutrient and has an important impact on the chemistry of the atmosphere. We used selective inhibitors and a glucose amendment in a factorial design to determine the relative contributions of autotrophic ammonium oxidizers, autotrophic nitrite oxidizers, and heterotrophic nitrifiers to nitric oxide (NO) and nitrous oxide (N(2)O) emissions from aerobically incubated soil following the addition of 160 mg of N as ammonium sulfate kg. Without added C, peak NO emissions of 4 mug of N kg h were increased to 15 mug of N kg h by the addition of sodium chlorate, a nitrite oxidation inhibitor, but were reduced to 0.01 mug of N kg h in the presence of nitrapyrin [2-chloro-6-(trichloromethyl)-pyridine], an inhibitor of autotrophic ammonium oxidation. Carbon-amended soils had somewhat higher NO emission rates from these three treatments (6, 18, and 0.1 mug of N kg h after treatment with glucose, sodium chlorate, or nitrapyrin, respectively) until the glucose was exhausted but lower rates during the remainder of the incubation. Nitrous oxide emission levels exhibited trends similar to those observed for NO but were about 20 times lower. Periodic soil chemical analyses showed no increase in the nitrate concentration of soil treated with sodium chlorate until after the period of peak NO and N(2)O emissions; the nitrate concentration of soil treated with nitrapyrin remained unchanged throughout the incubation. These results suggest that chemoautotrophic ammonium-oxidizing bacteria are the predominant source of NO and N(2)O produced during nitrification in soil.     

氢醌和双氰胺对种稻土壤N2O和CH4排放的影响

通过盆栽试验,研究了脲酶抑制剂氢醌（ＨＱ）、硝化抑制剂双氰胺（ＤＣＤ）及二者的组合（ＨＱ＋ＤＣＤ）对种稻土壤Ｎ２Ｏ和ＣＨ４排放的影响．结果表明,在未施麦秸粉时,所有施抑制剂的处理均较单施尿素的能显著减少水稻生长期供试土壤Ｎ２Ｏ和ＣＨ４的排放．特别是ＨＱ＋ＤＣＤ处理,其Ｎ２Ｏ和ＣＨ４排放总量分别约为对照的１／３和１／２．而在施麦秸粉后,该处理的Ｎ２Ｏ排放总量为对照的１／２,但ＣＨ４排放总量却较少差别．不论是Ｎ２Ｏ还是ＣＨ４的排放总量,施麦秸粉的都比未施的高出１倍和更多．因此,单从土壤源温室气体排放的角度看,将未腐熟的有机物料与尿素共施,并不是一种适宜的施肥制度．供试土壤的Ｎ２Ｏ排放通量,与水稻植株的ＮＯ－３Ｎ含量和土表水层中的矿质Ｎ量分别呈显著的指数正相关和线性正相关;ＣＨ４的排放通量则与水稻植株的生长量和土表水层中的矿质Ｎ量呈显著的线性负相关．在Ｎ２Ｏ与ＣＨ４的排放间,未施麦秸粉时存在着定量的相互消长关系;施麦秸粉后,虽同样存在所述关系,但难以定量化．