氮肥品种对亚热带土壤N2O排放的影响

以亚热带湿热地区红壤性旱地(SU),灌丛(GB),林地(QF)为研究对象,通过在30℃和60%WHC水分条件下,35 d的培养试验,研究了外源铵态氮输入对土壤N2O排放的影响。结果表明,对于pH较高的土壤SU(pH=6.27),施用硫铵、尿素和碳酸氢铵后,硝态氮累积量和N2O排放量均高于未施氮的处理,且随施N量增加而增加。对于酸性土壤GB(pH=4.82)和QF(pH=4.46),施用硫铵明显地抑制硝化作用,但却极大地促进N2O排放;施用尿素和碳酸氢铵对硝化作用有微弱的促进作用或无明显的影响,N2O的排放则略低于对照或无明显差异。酸性土壤中,加入不同类型的氮肥后,N2O排放量与硝态氮含量的比例与加入氮肥后测定的土壤pH具有显著的负相关关系。氮肥品种影响N2O排放量与硝态氮产生量比例的机理值得进一步研究。     

两种水分含量下生物质炭对黑土N2O排放及硝化反硝化基因丰度的影响

生物质炭对土壤结构改良、土壤肥力提升和农田温室气体排放具有重要意义。本研究以吉林省梨树县典型黑土为研究对象，通过培育实验，研究不同土壤水分含量（40%WHC和100%WHC）下，生物质炭种类（玉米秸秆生物质炭和稻壳生物质炭）和施加量（0%、1%和4%（w/w））对黑土N2O排放及硝化反硝化功能基因丰度的影响。结果表明，随着秸秆生物质炭施加量的增加，土壤N2O排放呈下降趋势，4%高量秸秆生物质炭添加下，土壤N2O排放量仅为1%低量秸秆生物质炭添加下的33.9%。同时土壤NO- 3-N也表现出一致性规律，4%高量生物质炭添加下土壤NO- 3-N含量显著低于1%低量生物质炭。在100%WHC土壤水分状况下，玉米秸秆生物质炭显著增加了土壤N2O排放，而稻壳生物质炭则显著降低了土壤N2O排放。高土壤水分显著促进了土壤N2O排放，进一步为实时荧光定量PCR结果所证实，高土壤水分通过增加nirS基因丰度进而促进了土壤反硝化作用过程，而4%高量稻壳生物质炭添加下nosZ基因丰度显著高于玉米秸秆生物质炭添加，表现出更强的N2O还原潜力。尽管amoA-AOA基因丰度在不同生物质炭添加量下并未发生显著变化，但amoA-AOB基因丰度在高量玉米秸秆生物质炭添加下显著下降。结果说明，土壤水分和生物质炭通过影响土壤硝化反硝化微生物的营养底物和代谢过程，进而影响土壤N2O排放特征。     

黄土性土壤剖面中N2O排放的研究初报

用田间原位土壤探头测定法和乙炔抑制未扰动土柱法 ,对黄土性土壤N2 O的排放进行了研究。试验结果表明 ,黄土性土壤N2 O的排放量存在着明显的季节和空间变异。季节变化与田间水分因子密切相关 ,N2 O高峰常出现在灌水 (降水 ) 3天后 ,施肥处理和对照的趋势完全一致。全年中八月份各土层N2 O浓度最高 ;在最高峰值时 ,施肥处理的N2 O浓度几乎是对照处理的 2 .5倍。土壤剖面中N2 O的浓度的顺序是 1 0cm <30cm <1 50cm <90cm <60cm ,以 60～90cm土层最高。影响黄土性土壤反硝化的主要因子是作为微生物能源和碳源的有机物质 ,在碳源充足时 ,土壤的硝态氮含量和水分因子是限制因子。     

不同水分条件下土壤N2O排放的动力学方程模拟

[目的]水分对土壤N₂O排放有重要影响。运用混合动力学方程模拟不同水分条件下土壤N₂O累积排放的过程,分析土壤水分对N₂O产生途径的影响及其变化规律,为通过改善土壤管理降低N₂O气体排放提供理论和实践指导。[方法]通过室内培养试验,研究了不同水分条件[40%WHC,60%WHC,80%WHC,100%WHC和淹水处理,WHC(田间持水量)]下土壤N₂O排放特征、硝铵态氮含量和氧气消耗动态变化。[结果](1)N₂O排放速率24 h时达到最大,淹水处理[3.46μg/(kg·h)]是其他处理的54.5～178.9倍。(2)土壤N₂O累积排放量均随着培养时间的延长而增加,淹水处理的快速上升阶段为前48 h,而其他处理为前96 h。培养结束时的土壤N₂O累积排放量,淹水处理(44.6μg/kg)分别是40%WHC,60%WHC,80%WHC和100%WHC的67.1,29.2,20.8,10.4倍。(3)除淹水条件下,伪...     

硝化抑制剂和通气调节对土壤N2O排放的影响

采用室内培养方法,研究了土壤水分含量和温度对硝化反应速度、N2O排放及施用硝化抑制剂(N-Serve)和土壤掺砂对N2O排放的影响。结果表明,硝化反应速度随温度升高而加快,30℃时反应进行最快;水分对硝化反应速度的影响不显著。N2O排放通量随温度和水分含量升高而加大,最高排放通量出现在水分含量28.5%,20℃或30℃时。30℃、低水分(14.2%)时,N2O排放量较低,15d累积排放量为126.4.mg/kg,且主要来自硝化反应,施用N-Serve可使总排放量减少65.0%;水分含量增加到28.5%,反硝化反应发生,N2O排放量急剧增加,15d累积排放量达764.4.mg/kg;施用砂子或N-Serve,总排放量分别减少82.9%、62.1%。因此,低水分时,施用N-Serve可抑制硝化反应;高水分时,施用砂子或砂子与N-Serve配合,可有效抑制N2O排放。     

控释肥施用对小麦生长期N2O排放的影响

通过田间试验,采用静态箱法研究不同施氮水平下控释肥和尿素(N 0、100、200、270 kg hm-2)对麦季N2O排放的影响。结果表明,与对照相比,整个小麦生长季N2O排放量均随尿素和控释肥施用量的增加呈指数增加(32%～164%,p<0.05),但控释肥处理增加程度则较尿素处理缓和;施用控释肥可以有效抑制小麦生长季N2O排放(p<0.05),控释肥对N2O的减排量随着施氮量的增加而增加。小麦产量随尿素施用量的增加呈抛物线增加(24%～43%,p<0.05),随控释肥施用量的增加亦呈抛物线增加(30%～45%,p<0.05);与施用相同水平尿素相比,施用控释肥的小麦产量略有增加,但无显著差异(p>0.05)。单位产量N2O排放量随尿素施用量的增加而呈指数增加(31%～114%,p<0.05),随控释肥施用量的增加而呈抛物线增加(2%～50%,p<0.05);施用控释肥可以有效抑制小麦生长季单位产量N2O排放(p<0.05),控释肥对单位产量N2O的减排量随着施氮量的增加而增加。各处理N2O排放量与土壤水分存在显著正相关(p<0.05),与土壤NH4+-N、NO3--N浓度和土温不呈明显线性关系(p>0.05)。     

不同施肥处理对稻田氧化亚氮排放的影响

2004年在湖南省望城县黄金乡长期肥料监测站对不同施肥处理稻田中N2O排放通量进行了连续观测,发现不同施肥处理稻田中N2O排放季节变化具有一致的规律:生长中前期N2O排放量较小,晒田及之后排放量较大。各施肥处理N2O排放的差异早晚稻不同,早稻各处理间差异不显著,NPK处理排放量最大,为1.48kg.hm2;晚稻各处理差异极显著(p<0.01),NPKS处理排放量最大,为1.40kg.hm2;同是有机肥和化肥配施,早稻NKM处理N2O排放大于NPKS处理,两者差异不显著,而晚稻NPKS处理N2O排放远大于NKM处理,二者差异显著(p<0.05)。稻田水分状况也影响N2O排放,淹水期N2O排放较少,落干期N2O排放较多。     

不同耕作措施下土壤N2O排放及其农学效率

为评价不同耕作措施下华北平原农田土壤N2O排放及其农学效率,通过设置常规耕作秸秆还田(CT+)、常规耕作无秸秆还田(CT?)、免耕秸秆还田(NT+)、免耕无秸秆还田(NT?)4个处理田间定位试验,采用静态箱?气相色谱法测定分析了连续3个小麦生长期的表层土壤N2O排放及其主要相关因子,同时测定了小麦产量与氮吸收量等相关指标。结果表明:在4个处理下,小麦生长期内表层土壤N2O排放动态基本一致,而土壤N2O累积排放量却存在显著差异,而且耕作方式与秸秆还田存在显著的互作效应。在常规耕作和免耕措施下,单位面积土壤N2O累积排放量均表现为秸秆还田土壤显著高于无秸秆还田土壤,CT+和NT+分别比CT?和NT?高26.2%和74.6%;在无秸秆还田条件下,土壤N2O排放量表现为常规耕作比免耕高42.4%。相关分析表明,土壤N2O排放通量与地下5 cm土壤温度、土壤孔隙充水率(WFPS)之间呈显著正相关关系,与土壤溶解性有机氮(DON)含量之间呈显著负相关关系。利用农学效率指标度量N2O排放量时可知,虽然小麦籽粒产量和氮肥偏生产力在各处理间没有达到显著性差异,但每生产1 kg小麦籽粒表层土壤N2O排放量为0.18~0.73 g N2O-N,每投入1 kg氮素表层土壤N2O排放量为5.1~18.0 g N2O-N,处理间存在显著差异;与单位面积土壤N2O排放量表现一致,单位籽粒产量N2O排放量和单位氮素投入N2O排放量均表现为无论是常规耕作还是免耕措施,秸秆还田土壤均显著高于秸秆不还田土壤,在秸秆不还田条件下,常规耕作土壤均显著高于免耕土壤。总之,免耕是有效减少土壤N2O排放的一种耕作措施。     

菜地土壤施用铵态氮肥后 N2O 排放来源及其动态

氧化亚氮(N2O)是重要的农业源温室气体,菜地土壤施肥量高、施肥次数多,且肥水同期,是重要的N2O排放源。采用室内培养实验,测定在70%田间持水量条件下菜地土壤施用铵态氮肥后3周内N2O排放动态,利用不同气体抑制剂(低浓度乙炔、纯氧、纯氦、纯氧+乙炔)对N2O排放过程抑制效果各不相同的特点,经合理组合计算得出自养硝化、硝化细菌的反硝化、生物反硝化等主要过程对土壤N2O排放的相对贡献及其动态,以探索菜地土壤施用铵态氮肥后土壤N2O排放的来源及动态。结果表明,(1)在70%田间持水量条件下,菜地土壤施用铵态氮肥后2d内(48h内)的N2O排放通量最高,为314.4ng·g-1·d-1,到第4天时N2O排放通量已迅速降至前两天的1/6,且随培养时间的延长其排放通量不断降低。(2)自养硝化作用是菜地施用铵态氮肥后N2O排放的主要来源,施肥培养后2周内的贡献率在50%以上,2周后其贡献率降至40%左右。(3)硝化细菌的反硝化作用对N2O排放的贡献主要在施铵氮后2d内,其贡献率达44%,之后其贡献率一直保持在14%~27%。反硝化作用对N2O排放的贡献随着土壤中铵态氮含量的下降和硝态氮含量的升高而逐渐从开始时不到1%增至30%,但由于施肥培养2周后N2O的排放通量绝对数值很低(仅为施肥后2d内排放高峰的1/20),故其对N2O排放的贡献有限。土壤N2O排放通量及其来源与土壤中铵态氮和硝态氮含量的动态变化密切相关,施用铵态氮肥后土壤短期内呈现酸化趋势。因此,合理控制硝化作用是有效控制菜地土壤N2O排放的关键措施。     

水热对三峡水库消落带退耕稻田土壤有机碳矿化的影响

采用模拟培养的方法,研究了不同水热条件对三峡水库消落带退耕稻田土壤有机碳(SOC)矿化的影响。试验共设3个培养温度(10、20和30℃)和4个水分梯度(40%田间持水量(WHC)、70%WHC、100%WHC和浅层淹水)。结果表明:1在66天培养期内,各培养温度(10~30℃)下,70%WHC、100%WHC和浅层淹水处理之间的SOC累积矿化量均无明显差异,其中10℃培养时40%WHC处理下的累积矿化量要显著低于70%WHC和100%WHC水分处理(P0.05),但与浅层淹水无明显差异,而20℃和30℃培养时40%WHC处理下的累积矿化量则要显著低于其他水分处理,表明相较于70%WHC的水分处理,40%WHC水分处理会抑制消落带退耕稻田SOC矿化,而高水分(100%WHC和浅层淹水)对SOC矿化则无明显促进和抑制作用。2在相同水分条件下,消落带退耕稻田SOC累积矿化量均随培养温度升高而增加。3高温下各水分处理之间的温度敏感性无显著差异,而低温下水分对温度敏感性有显著影响,低温浅层淹水处理下的Q10为2.33,显著高于40%WHC处理,与70%WHC和100%WHC处理之间无明显差异。且随着温度升高,浅层淹水下消落带退耕稻田SOC矿化的温度敏感性显著降低,而在土壤含水量≤100%WHC下则无明显变化。温度和水分均能显著影响SOC矿化,但二者无明显的交互效应。4双库一级矿化动力学模型拟合结果表明,水分和温度通过影响消落带退耕稻田土壤易分解有机碳含量和难分解有机碳的矿化速率,从而影响SOC矿化。     

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。     

Emission of nitrous oxide and carbon dioxide and dynamics of mineral N in wastewater sludge,vermicompost or inorganic fertilizer amended soil at different water contents: A laboratory study

Liming or vermicomposting eliminates pathogens from wastewater sludge, but might affect CO₂ and N₂O emissions when added to soil. Soil incubated at 40%, 60%, 80% and 100% of its water holding capacity (WHC) was amended with limed or unlimed wastewater sludge, vermicompost or inorganic fertilizer, while emissions of N₂O and CO₂ and mineral N concentrations were monitored in aerobic incubation experiment for 7 days. Application of unlimed wastewater sludge significantly increased the emission of CO₂ compared to the unamended soil, but not the other treatments except when unlimed wastewater sludge was added to soil incubated at 60% WHC. The emission of CO₂, was generally largest in soil incubated at 60% WHC and lowest in soil incubated at 100% WHC. The emission of N₂O after 1 day was significantly larger in soil amended with unlimed wastewater sludge compared to the other treatments, but not when soil was incubated at 100% WHC. The emission of N₂O increased with increased soil water content. The concentration of NH₄⁺ was largest in soil amended with limed or unlimed wastewater sludge and lowest in the unamended soil and soil water content had no clear effect on it. In soil incubated at 40%, 60% and 80% WHC, the largest amount of NO₃⁻ was found in soil amended with inorganic fertilizer and vermicompost and the lowest in the soil amended with unlimed wastewater sludge. The concentration of NO₃⁻ in soil decreased when the soil water content increased in all treatments, except in the soil amended with unlimed wastewater sludge. It was found that water content affected the emission of CO₂ of N₂O and the concentration of NO₃⁻, but not the amount of NH₄⁺ and NO₂⁻ in soil. Application of unlimed wastewater sludge increased the emissions of CO₂ and N₂O and the concentrations of NH₄⁺, but decreased the amount of NO₃⁻ in soil.     

Nitrous oxide production at different soil moisture contents in an arable soil in China

Abstract

Laboratory incubations were conducted to investigate nitrous oxide (N₂O) production from a subtropical arable soil (Typic Plinthodults) incubated at different soil moisture contents (SMC) and with different nitrogen sources using a 10% (v/v) acetylene (C₂H₂) inhibitory technique at 25°C. The production of N₂O and CO₂ was monitored during the incubations and changes in the contents of KCl-extractable NO^? ₃-N and NH⁺ ₄-N were determined. The production of N₂O increased slightly with an increase in SMC from 40% water-holding capacity (WHC) to 70% WHC, but increased dramatically at 100% WHC. After incubation the NO^? ₃-N content increased even at a SMC of 100% WHC. At a SMC of 100% WHC, the addition of NH⁺ ₄-N promoted the production of N₂O and CO₂, whereas the addition of NO^? ₃-N decreased N₂O production. Compared with the incubation without C₂H₂, the presence of C₂H₂ increased NH⁺ ₄-N content, but decreased NO^? ₃-N content, and there was no significant difference in N₂O production. These results indicate that heterotrophic nitrification contributes to N₂O production in the soil.     

秸秆还田对灌溉玉米田土壤反硝化及N2O排放的影响

运用乙炔抑制技术研究了不同施氮水平下秸秆还田对灌溉玉米田土壤反硝化反应和氧化亚氮(N2O)排放的影响。结果表明,土壤反硝化速率及N2O的排放受氮肥施用、秸秆处理方式及其交互作用的显著影响。与秸秆燃烧相比,不施氮或低施氮水平时,秸秆还田可刺激培养初期反硝化反应速率及N2O排放,增加培养期间N2O平均排放通量;高施氮水平时,秸秆还田可降低反硝化反应速率及反硝化过程中的N2O排放。秸秆还田可降低反硝化中N2O/N2的比例。     

有机无机氮肥配施下洛阳烟田土壤N2O排放特点及其控制因素

随着农田化肥使用量的逐年增加和土壤退化问题日趋严重,农田温室气体排放关注度持续提高,为研究旱作植烟土壤N_2O排放特征及影响机理,设置6个田间试验处理,分别为CK0(不施肥处理)、CK1(100%无机氮)、T1(50%无机氮+50%饼肥氮)、T2(50%无机氮+50%羊粪肥氮)、T3(25%无机氮+75%饼肥氮)、T4(25%无机氮+75%羊粪肥氮),各处理施氮量均为45 kg/hm²,烟田施用基肥后起142天内测量不同处理土壤N_2O排放通量、硝态氮、铵态氮含量、根层温度和含水率。结果表明:(1)基肥施入后的3~7天内,土壤N_2O排放通量进入高峰,无机肥处理和有机无机肥配施处理的高峰期分别可维持20,9天,追肥后3天再次出现排放峰并持续9天,随后伴随烟株的生长发育,烟地N_2O排放通量逐渐趋向稳定。(2)基肥施用后仅1个月内N_2O累积排放量可达到总排放量的27.4%~32.6%;处理间N_2O排放量和排放系数均表现为无机>有机+无机(1∶1)>有机+无机(3∶1),无机肥配施有机肥明显降低了肥料中氮素以N_2O形态的损失量;与无机肥相比,T1和T2烟叶产量分别增加9.44%和6.37%,T1、T2、T3和T4处理的N_2O排放强度有着不同程度的降低。(3)主成分分析结果显示,在不施肥烟地中0—5 cm土壤温度和含水率是N_2O排放通量主导因子,利用相关性分析此环境下温度和水分分别与N_2O排放通量间呈现显著和极显著正相关关系;施肥后土壤铵态氮含量和土壤含水率是烟地N_2O排放通量的主导因子且相关性分析均呈现极显著正相关关系。综上,旱地植烟土壤N_2O排放受氮肥种类影响较大,施肥后N_2O排放通量对土壤温度响应减弱,主要受土壤铵态氮含量和含水量的影响;在总氮量相同情况下,有机无机肥配施比例为1∶1时明显降低土壤N_2O排放并提高了产量,该比例饼肥和羊粪肥处理分别将烟地N_2O排放强度降低20.4%和23.7%。     

Nitrous oxide emission as affected by changes in soil water content and nitrogen fertilization

Nitrous oxide emission was measured in laboratory incubations of an alluvial soil (58% clay, pH 7.4). The soil was amended with 40 mg N kg⁻¹ as NaNO₃ or NH₄Cl, or with NaCl as a control. Each fertilization treatment was adjusted to three different water contents: constant 60% WHC (water-holding capacity), constant 120% WHC, and water content alternating between 60 and 120% WHC. During an 8-day incubation period N₂O emission rates and inorganic nitrogen concentrations in soil (NH₄⁺, NO₂⁻, NO₃⁻) were determined at regular intervals. In the control and after nitrate application small N₂O emission rates occurred with only minor variations over time, and no differences between the water treatments. In contrast, with ammonium application N₂O emission rates were much higher during the first two days of incubation, with peaks in the constant 60% WHC and 120% WHC at day 1 and in the changing-water treatment at day 2, when the first wet period (120% WHC) was completed. This N₂O peak in the changing-water treatment was 4 to 9 times higher than with constant WHC and occurred when both, NH₄⁺ and NO₂⁻ concentrations declined sharply. Thus, this N₂O emission flush can be attributed to nitrifier denitrification. After the second rewetting of the NH₄⁺-amended soil no further N₂O emission peak was observed, being in accordance with small NH₄⁺ and NO₂⁻ concentrations in soil at that time. The unexpectedly small N₂O fluxes in the constant 120% WHC treatment after nitrate application were probably caused by the reduction of N₂O to N₂ under the prevailing conditions. It can be concluded that continuous wetting or flooding of a soil is an effective measure to reduce N₂O emissions immediately after the application of NH₄⁺ fertilizers.     

下辽河平原潮棕壤撂荒地和人工林N2O、CH4排放研究

采用静态箱(暗箱)气相色谱法对下辽河平原潮棕壤撂荒地和人工林N2O、CH4排放进行了为期1年的原位测量,同时测量了土壤温湿度、气温,土壤NO3-N、NH4 -N含量等相关因子.结果表明,在观测期间内人工林地土壤的N2O排放通量明显高于撂荒地.撂荒地是大气CH4的源,而人工林则是CH4的汇.对人工林的观测结果表明,N2哦O排放与CH4排放之间存在负相关关系(R2=-0.351,p＜0.05,n=36);而撂荒地两种气体排放之间无明显相关关系.N2O排放通量和温度变化有很好的相关性.当土壤含水量在200 g/kg以上时,土壤含水量与CH4气体排放具有较好的正相关关系.     

稻秆还田方式对麦田N2O排放的影响

通过田间试验研究了3种稻秆还田方式(表面覆盖、均匀混施和原位焚烧)对麦田N2O排放的影响.结果表明,不同稻秆还田方式麦田N2O排放量为:表面覆盖＞对照(不施稻秆)＞均匀混施＞原位焚烧.与对照相比,稻秆表面覆盖显著增加麦田N2O排放量,而均匀混施和原位焚烧显著减少N2O排放量.N2O排放通量与土壤温度无显著相关性,与土壤水分呈显著正相关.与对照相比,稻秆均匀混施使小麦产量显著增加,表面覆盖和原位焚烧对小麦产量无显著影响.     

高氮和NO2-对中亚热带森林土壤N2O和NO产生的影响

利用15N同位素标记方法,研究在两种水分条件即60%和90% WHC下,添加硝酸盐(NH4NO3, 300mgN kg-1)和亚硝酸盐(NaNO2, 1mgN kg-1)对中亚热带天然森林土壤N2O和NO产生过程及途径的影响。结果表明,在含水量为60% WHC的情况下,高氮输入显著抑制了N2O和NO的产生(p<0.01);但当含水量增为90% WHC后,实验9h内抑制N2O产生,之后转为促进。所有未灭菌处理在添加NO2-后高氮抑制均立即解除并大量产生N2O和NO,与对照成显著差异(p<0.01)。在60% WHC条件下,这种情况维持时间较短(21h),但如果含水量高(90% WHC)这种情况会持续很长时间(2wk以上),说明水分有效性的提高和外源NO2-在高氮抑制解除中起到重要作用。本实验中N2O主要来源于土壤反硝化过程,而且加入未标记NO2-后导致杂合的N2O(14N15NO)分子在实验21h内迅速增加,表明这种森林土壤的反硝化过程可能主要是通过真菌的“共脱氮”来实现,其贡献率可多达80%以上。Spearman等级相关分析表明未灭菌土壤NO的产生速率与N2O产生速率成显著正相关性(p<0.05),土壤含水量越低二者相关性越高。灭菌土壤添加NO2-能比未灭菌土壤产生更多的NO,但却几乎不产生N2O,表明酸性土壤的化学反硝化对NO的贡献要大于N2O。     

温室菜园土壤氮矿化和微生物群落对水分的响应

Soil drying and wetting impose significant influences on soil nitrogen (N) dynamics and microbial communities. However, effects of drying-wetting cycles, while common in vegetable soils, especially under greenhouse conditions, have not been well studied. In this study, two greenhouse vegetable soils, which were collected from Xinji (XJ) and Hangzhou (HZ), China, were maintained at 30% and 75% water-holding capacity (WHC), or five cycles of 75% WHC followed by a 7-day dry-down to 30% WHC (DW). Soil inorganic N content increased during incubation. Net N mineralization (Nmin), microbial activity, and microbial biomass were significantly higher in the DW treatment than in the 30% and 75% WHC treatments. The higher water content (75% WHC) treatment had higher Nmin, microbial activity, and microbial biomass than the lower water content treatment (30% WHC). Multivariate analyses of community-level physiological profile (CLPP) and phospholipid fatty acid (PLFA) data indicated that soil moisture regime had a significant effect on soil microbial community substrate utilization pattern and microbial community composition. The significant positive correlation between Nmin and microbial substrate utilization or PLFAs suggested that soil N mineralization had a close relationship with microbial community.