南方稻田活性氮损失途径及其影响因素

基于文献数据,研究了南方不同稻区水稻生长期氧化亚氮排放(N₂O排放)、硝态氮或铵态氮淋洗(N淋洗)、硝态氮或铵态氮径流(N径流)、氨挥发(NH₃挥发)的差异及其影响因素.结果表明: N₂O排放、N淋洗和N径流主要发生在长江流域单季稻区,损失量分别为1.89、6.4和10.4 kg N·hm^-2,损失率分别为0.8%、3.8%和5.3%,较高施氮量和稻田土壤干湿交替可能是主要原因;NH₃挥发主要发生在华南晚稻,损失量和损失率分别为54.9 kg N·hm^-2和35.2%,晚稻生长期较高的温度可能是NH₃挥发较大的主要原因.田间优化管理措施减少某一途径氮损失的同时可能会增加另一种途径氮素损失,实际生产中应综合考虑田间管理措施对各种活性氮损失的影响,活性氮损失量随着水稻产量水平的提高而增加,主要是因为施氮量也在逐渐增加.随着氮肥偏生产力的增加,N₂O排放、N淋洗和N径流损失率逐渐下降,因此,努力减小单位产量的氮损失,是协同提高作物产量和氮肥利用效率的重要途径.     

施肥对露地菜地氨挥发和氧化亚氮排放的影响

为探究施氮量和不同肥料调控措施对露地菜地土壤氨(NH₃)挥发和氧化亚氮(N₂O)排放的影响,在华北地区典型露地菜地设置了不同施氮水平和肥料调控措施的田间试验.结果表明: 春播黄瓜生育期内减氮20%和50%分别比常规施氮量降低氨挥发25.7%和48.0%;添加抑制剂(脲酶抑制剂+硝化抑制剂)和生物炭分别比等氮量氮肥处理氨挥发降低10.0%和6.1%;春播黄瓜生育期内减氮20%和50%分别使N₂O排放量比常规施肥处理降低28.8%和61.0%;等氮量条件下添加联合抑制剂使N₂O排放降低58.9%,而添加生物炭处理的N₂O排放增加14.1%;在同样的条施覆土施肥方法下,与纯化学氮肥处理相比,有机肥替代30%氮肥对氨挥发和N₂O减排的作用效果都不显著.对于集约化菜地,合理控制氮肥用量是降低土壤氨挥发及N₂O排放的最有效措施.     

不同氮肥喷涂吡啶对夏玉米田氮素利用及土壤N2O排放的影响

为减少土壤N₂O排放,提高作物氮素利用,采用田间试验法研究了不同氮肥用量喷涂一定比例的吡啶(0、180、270、360 kg N·hm^-2)对夏玉米生育期内土壤N₂O排放和氮素表观损失、籽粒产量及氮素利用的影响.结果表明:不同氮肥用量下喷涂吡啶的土壤N₂O排放主要集中在播种-苗期和拔节-抽雄期,基肥和追肥后均会出现显著的土壤N₂O排放通量高峰.随氮肥用量增加,玉米产量不断增加,但270和360 kg N·hm^-2间无显著差异,2种施氮量下的玉米分别净增收5209和5426元·hm^-2.与不施氮肥比,各施氮处理下的玉米籽粒吸氮量提高幅度为109.6%～134.1%.各处理间的氮肥农学效率和氮肥利用率均以氮肥喷涂吡啶270 kg N·hm^-2较大,而土壤氮素表观损失较小.氮肥喷涂吡啶在270 kg N·hm^-2时玉米增产增收,氮肥利用效率较高,土壤N₂O排放和氮素表观损失较少,是一种较为合理的氮肥调控施用技术.     

不同氮肥喷涂吡啶对夏玉米田氮素利用及土壤N2O排放的影响

为减少土壤N₂O排放,提高作物氮素利用,采用田间试验法研究了不同氮肥用量喷涂一定比例的吡啶(0、180、270、360 kg N·hm^-2)对夏玉米生育期内土壤N₂O排放和氮素表观损失、籽粒产量及氮素利用的影响.结果表明:不同氮肥用量下喷涂吡啶的土壤N₂O排放主要集中在播种-苗期和拔节-抽雄期,基肥和追肥后均会出现显著的土壤N₂O排放通量高峰.随氮肥用量增加,玉米产量不断增加,但270和360 kg N·hm^-2间无显著差异,2种施氮量下的玉米分别净增收5209和5426元·hm^-2.与不施氮肥比,各施氮处理下的玉米籽粒吸氮量提高幅度为109.6%～134.1%.各处理间的氮肥农学效率和氮肥利用率均以氮肥喷涂吡啶270 kg N·hm^-2较大,而土壤氮素表观损失较小.氮肥喷涂吡啶在270 kg N·hm^-2时玉米增产增收,氮肥利用效率较高,土壤N₂O排放和氮素表观损失较少,是一种较为合理的氮肥调控施用技术.     

持续施用缓/控释尿素条件下水田土壤NH3挥发与N2O排放特征

以持续9年施用不同缓／控释尿素的水田棕壤为试验对象,以普通大颗粒尿素为对照,研究了持续施用不同缓／控释尿素条件下水田土壤NH₃挥发与N₂O排放特征.结果表明: 与普通大颗粒尿素(U)相比,除1% 3,4－二甲基吡唑磷酸盐(DMPP)+U处理 NH₃挥发增加了25.8%外,其他缓／控释尿素肥料处理对NH₃有明显的减排效果.树脂包膜尿素(PCU)对NH₃减排效果最明显,为73.4%,硫包膜尿素(SCU)为72.2%,0.5% N-丁基硫代磷酰三胺(NBPT)+1% DMPP+U为71.9%,1% 氢醌(HQ)+3% 双氰胺(DCD)+U为46.9%,0.5% NBPT+U为43.2%,1% HQ+U为40.2%,3% DCD+U为25.5%, 1% DMPP均与施用普通大颗粒尿素差异显著;所有缓／控释尿素处理与对照相比均可显著减少N₂O排放.1% DMPP+U对N₂O减排效果最明显,为74.9%,PCU为62.1%,1% HQ+3% DCD+U为54.7%,0.5% NBPT+1% DMPP+U为42.2%,3% DCD+U为35.9%,1% HQ+U为28.9%,0.5% NBPT+U为17.7%,SCU为14.5%,均与施用普通大颗粒尿素差异显著.比较0.5% NBPT+1% DMPP+U、SCU、PCU对NH₃和N₂O减排的综合效果,3种肥料作用相近,且均明显优于其他处理,但包膜材料的成本较抑制剂高数倍.因此,同时添加脲酶和硝化抑制剂的缓释尿素是减少水田氮素损失及环境污染的首选氮肥.     

全膜双垄沟播玉米耗水特性和籽粒产量对不同氮素形态配比的响应

为优化陇中干旱、半干旱地区全膜双垄沟播玉米的氮肥运筹,提高玉米籽粒产量,通过大田试验,研究了不同氮素形态配比(NO₃^--N/NH₄⁺-N)[N₁(1∶0)、N₂(1∶1)、N₃(1∶3)、N₄(3∶1)]对旱地全膜双垄沟播玉米耗水特性、产量和水分利用效率的影响.结果表明: 不同氮素形态配比显著影响玉米0～200 cm土层的土壤贮水量,且N₄处理土壤贮水量最低.N₄处理农田总耗水量最高,较N₁、N₂、N₃分别显著增加了2.9%、1.9%、0.9%(2015)和2.3%、1.4%、2.2%(2017).玉米籽粒产量和水分利用效率(WUE)在3个生长季均表现为N₄处理最高,籽粒产量较其他处理分别高出3.3%～9.9%(2015)、3.5%～24.2%(2016)和8.3%～36.1%(2017),WUE则较其他处理分别高出1.6%～6.8%、4.9%～21.8%和6.6%～32.9%.N₄处理下玉米的氮肥偏生产力显著高于其他处理,然后依次为N₃、N₂和N₁.综合考虑,NO₃^--N/NH₄⁺-N=3∶1是适宜陇中干旱、半干旱地区全膜双垄沟播玉米增产的氮肥运筹措施.     

我国北方几种玉米和设施菜地土壤的N2O和N2排放特征

为了探究旱地土壤施入氮肥后的气态氮(N₂O和N₂)损失规律,本研究通过室内好氧培养试验(60 d,25 ℃,80%孔隙含水量),运用¹⁵N同位素示踪技术,研究了4个玉米地土壤(哈尔滨、沈阳、栾城、寿光)和2个设施菜地土壤(沈阳、寿光)在施入尿素后的氮转化、N₂O和N₂排放动态。试验中尿素添加量为167 mg N·kg^-1,以模拟田间氮肥施用量200 kg N·hm^-2。结果表明: 在4个玉米地土壤中,尿素施用60 d内N₂O累积排放量为寿光(20 mg N·kg^-1)>栾城(14 mg N·kg^-1)>沈阳(5 mg N·kg^-1)>哈尔滨(0.5 mg N·kg^-1),N₂累积排放量为栾城(176 mg N·kg^-1)>沈阳(106 mg N·kg^-1)>寿光(75 mg N·kg^-1)>哈尔滨(12 mg N·kg^-1);在2个设施菜地土壤中,寿光土壤N₂O累积排放量(21 mg N·kg^-1)是沈阳(2 mg N·kg^-1)的10倍,而两个站点N₂累积排放量分别为28和24 mg N·kg^-1。不同土壤N₂O排放占两种气体排放总量的5%～40%,其中寿光土壤(30%～40%)显著高于其他样地土壤(1%～10%)。在土壤排放的N₂O和N₂中,土壤氮库分别贡献了56%和61%,高于添加当季氮肥的贡献率。相关分析表明,N₂O累积排放量与本底土壤pH呈正相关,说明土壤本底pH可能是调控不同旱地土壤N₂O和N₂排放的重要环境因子。在华北碱性土壤区,采用能降低土壤pH值的措施可能具有较好的气态氮减排效果。     

土壤水分对土壤产生气态氮的厌氧微生物过程的影响

气态氮[一氧化氮(NO)、氧化亚氮(N₂O)和氮气(N₂)]的释放是土壤氮损失的一种重要途径。硝化和反硝化作用是土壤气态氮损失的主要微生物过程,但是异养硝化作用、共反硝化作用和厌氧氨氧化过程对土壤气态氮损失的贡献尚不清楚。本研究利用¹⁵N标记和配对法,结合硝化抑制剂双氰胺(DCD),通过土壤培养试验来量化厌氧条件下各种微生物过程对NO、N₂O和N₂产生的贡献。结果表明: 在厌氧条件下培养24 h后,土壤孔隙含水率为65%时,3种气体总的¹⁵N回收率最高,占加入¹⁵N总量的20.0%。反硝化过程对NO、N₂O和N₂产生的贡献率分别为49.9%～94.1%、29.0%～84.7%和58.2%～85.8%,是产生3种气体的主要过程。异养硝化过程也是产生NO和N₂O的重要过程,特别是在土壤孔隙含水率很低时(10%)对两种气体产生的贡献率分别为50.1%和42.8%。,共反硝化过程对N₂O产生的贡献率为10.6%～30.7%,共反硝化和厌氧氨氧化过程对N₂产生的总贡献率为14.2%～41.8%,表明共反硝化过程在N₂O和N₂产生中的作用不可忽视。¹⁵N标记和配对法是区分气态氮损失的各种微生物过程的有效手段。     

黄河口不同恢复阶段湿地土壤N2O产生过程对氮输入的响应

以黄河口生态恢复前后未恢复区(R₀)、2007年恢复区(R₂₀₀₇)和2002年恢复区(R₂₀₀₂)的芦苇湿地为研究对象,研究了不同形态氮输入对湿地土壤N₂O产生过程的影响与贡献.结果表明: 硝态氮(NO₃^--N)输入对恢复区湿地土壤N₂O总产生量的影响远远大于铵态氮(NH₄⁺-N),但两者均抑制了R₀土壤的N₂O总产生量.尽管NO₃^--N输入对R₂₀₀₂表层土壤N₂O总产生量的影响明显大于R₂₀₀₇,但二者的N₂O产生量均随氮输入量的增加而增加.恢复区湿地土壤的反硝化作用和硝化细菌反硝化作用受NO₃^--N输入的影响明显,而R₀土壤产生N₂O的生物过程受其影响并不显著.尽管NH₄⁺-N输入对湿地土壤N₂O的总产生量影响不大,但其输入整体促进了R₀ 土壤的硝化细菌反硝化作用、R₂₀₀₇土壤的硝化作用和R₂₀₀₂土壤的非生物作用.比较而言,NO₃^--N输入对R₀、R₂₀₀₇和R₂₀₀₂湿地土壤N₂O产生的非生物作用主要表现为抑制,NH₄⁺-N输入则整体提高了R₀和R₂₀₀₂湿地土壤非生物作用的N₂O产生量,这与不同形态氮输入对土壤pH的调节作用密切相关.研究发现,NO₃^--N输入大大增加了湿地土壤的N₂O总产生量,改变了原有湿地土壤生物作用和非生物作用的贡献模式,故生态恢复工程导致的营养盐输入(NO₃^--N)应受到特别关注.     

黄河口不同恢复阶段湿地土壤N2O产生过程对氮输入的响应

以黄河口生态恢复前后未恢复区(R₀)、2007年恢复区(R₂₀₀₇)和2002年恢复区(R₂₀₀₂)的芦苇湿地为研究对象,研究了不同形态氮输入对湿地土壤N₂O产生过程的影响与贡献.结果表明: 硝态氮(NO₃^--N)输入对恢复区湿地土壤N₂O总产生量的影响远远大于铵态氮(NH₄⁺-N),但两者均抑制了R₀土壤的N₂O总产生量.尽管NO₃^--N输入对R₂₀₀₂表层土壤N₂O总产生量的影响明显大于R₂₀₀₇,但二者的N₂O产生量均随氮输入量的增加而增加.恢复区湿地土壤的反硝化作用和硝化细菌反硝化作用受NO₃^--N输入的影响明显,而R₀土壤产生N₂O的生物过程受其影响并不显著.尽管NH₄⁺-N输入对湿地土壤N₂O的总产生量影响不大,但其输入整体促进了R₀ 土壤的硝化细菌反硝化作用、R₂₀₀₇土壤的硝化作用和R₂₀₀₂土壤的非生物作用.比较而言,NO₃^--N输入对R₀、R₂₀₀₇和R₂₀₀₂湿地土壤N₂O产生的非生物作用主要表现为抑制,NH₄⁺-N输入则整体提高了R₀和R₂₀₀₂湿地土壤非生物作用的N₂O产生量,这与不同形态氮输入对土壤pH的调节作用密切相关.研究发现,NO₃^--N输入大大增加了湿地土壤的N₂O总产生量,改变了原有湿地土壤生物作用和非生物作用的贡献模式,故生态恢复工程导致的营养盐输入(NO₃^--N)应受到特别关注.     

Gaseous nitrogen losses from 15N‐ammonium and plant material amended great basin desert surface soils

Gaseous nitrogen losses from ¹⁵NH₄ ⁺ that was exogenously applied to desert surface soils which were then incubated under aerobic conditions for 35 days at constant 25% moisture reached 81% with plant material added and 75% without an exogenous carbon source. At a decreasing moisture regime, the respective values were 79% and 87%. The losses were attributed to denitrification and, partially, to dissimilatory N₂O release during nitrification. Ammonia volatilization reached a plateau after 4 days, did not exceed 5% of the total ¹⁵NH₄ ⁺ added, and was significantly higher in the plant interspace soils than in the canopy soils.     

Effect of Molybdenum and Inorganic Nitrogen on Molybdenum Redistribution in Black Gram (Vigna mungo L. Hepper) with Particular Reference to Seed Fill

Seeds used to plant a crop may contain sufficient molybdenum(Mo) to prevent subsequent Mo deficiency in the crop even whenthey are sown on Mo deficient soils. However, little is knownabout either the sources of the Mo acquired by the seed, orthe timing of its redistribution during seed development. Aglasshouse experiment was set up to examine the effect of Mosupply and nitrogen source on the redistribution of Mo withinblack gram, from full flowering to seed maturity. Treatmentscomprised two sources of N (symbiotic N₂fixation, NH₄NO₃), twolevels of Mo supply [nil (-Mo), 0.64 mg Mo kg^-1soil (+Mo)] andfour harvests (full flowering, early pod setting, late pod fillingand seed maturity). The redistribution of Mo in black gram wasexamined by determining changes over time in the content ofMo in plant parts at each growth stage. Molybdenum supply and the plant growth stage strongly affectedthe redistribution of Mo to the seed. In -Mo plants relianton symbiotic N₂fixation, Mo redistributed from roots, stemsand leaves was the only source of Mo for reproductive developmentsince, from full flowering until maturity, there was no netincrease in whole plant Mo. For pod and early seed development,the roots were the major source of Mo in -Mo plants. After latepod filling, nodules replaced roots as the major source of Mofor seed fill in -Mo plants. By contrast, for +Mo plants relianton symbiotic N₂fixation, Mo taken up from the soil after fullflowering could have supplied nearly 50% of the seed Mo. Themajor sources of Mo for seed filling in +Mo plants were middlestem leaves during early podding, and middle stems and pod wallsfrom late podding. Supplying NH₄NO₃to plants from sowing had little effect on Modistribution or redistribution in +Mo black gram plants. However,in -Mo plants it accelerated the loss of Mo from middle stemsand their leaves compared to nodulated plants. Black gram; Vigna mungo L. Hepper; distribution; molybdenum; nitrogen; nodules; redistribution; seed fill     

Effectiveness of Lotus Root Nodules: III. EFFECT OF COMBINED NITROGEN ON NODULE EFFECTIVENESS AND FLAVOLAN SYNTHESIS IN PLANT ROOTS

When grown in a nutrient solution containing combined nitrogen(NH₄NO₃), Lotus pedunculatus and L. tenuis seedlings inoculatedwith a fast-growing strain of Rhizoblum (NZP2037) did neitherdevelop root nodules nor develop flavolans in their roots. Incontrast, the roots of nodulated seedlings growing in a nitrogen-freenutrient solution contained flavolans. Flavolan synthesis coincidedwith root nodule development on these plants. When added as a single dose, high concentrations of NH₄NO₃ (5and 10 mg N per plant) stimulated the growth of L. pedunculatusplants but suppressed nodulation and nitrogen fixation. In contrastthe continued supply of a low concentration of NH₄NO₃ (1?0 mgN d^–1 per plant) stimulated nitrogen fixation by up to500%. This large increase in nitrogen fixation was associatedwith a large increase in nodule fresh weight per plant, a doublingof nodule nitrogenase activity, and a lowering of the flavolancontent of the plant roots. The close relationship between nitrogendeficiency, nodule development, and flavolan synthesis in L.pedunculatus meant that it was not possible (by nitrogen pretreatmentof plants) to alter the ineffective nodule response of a Rhizobiumstrain (NZP2213) sensitive to the flavolan present in the rootsof this plant.     

Response of mycorrhizal seedlings of SW Australian sandplain Epacridaceae to added nitrogen and phosphorus

The responses of seedlings of four species of southwestern Australiansandplain Epacridaceae to added phosphate (P), added NH₄N0₃(N) or Complete nutrients were studied in glasshouse pot cultureusing cores of habitat soil as rooting substrate. Positive responsesto N and Complete nutrients were evident for three species interms of shoot height and shoot dry weight in comparison withControl plants supplied only with deionized water, but no speciesresponded significantly in its shoot growth to P. Root dry weightwas generally less in Complete and N treatments compared toP and Control, leading to considerably higher shoot: root ratiosin the former two treatments. There was no effect of treatmenton infection intensity of hair roots. Root xylem sap compositionshowed greatly elevated levels of nitrogen in the Complete andN treatments and of phosphate in the P treatment. Ammonium comprisedthe major nitrogenous solute of xylem in Control and P treatmentswhile nitrate levels exceeded ammonium in Complete and N treatments.Glutamine levels were particularly high in the P treatments.Labelling of the Complete or N treatments with ¹⁵NH₃ or ¹⁵NO₃(supplied as single labelled ammonium nitrate) indicated thatboth forms of N were taken up and incorporated into plant insolubleN. Key words: Epacridaceae, nitrogen, phosphorus, mycorrhiza, south-west Western Australia     

Partitioning of Nitrogen Derived from N2 Fixation and Reserves in Nodulated Medicago sativa L. During Regrowth

Nodul{macron}ted alfalfa plants were grown hydroponically. Inorder to quantify N₂ fixation and remobilization of N reservesduring regrowth the plants were pulse-chase-labelled with ¹⁵N.Starch and ethanol-soluble sugar contents were analysed to examinechanges associated with those of N compounds. Shoot removalcaused a severe decline in N₂ fixation and starch reserves within6 d after cutting. The tap root was the major storage site formetabolizable carbohydrate compounds used for regrowth; initiallyits starch content decreased and after 14 d started to recoverreaching 50% of the initial value on day 24. Recovery of N₂fixation followed the same pattern as shoot regrowth. Afteran initial decline during the first 10 d following shoot removal,the N₂ fixation, leaf area and shoot dry weight increased sorapidly that their levels on day 24 exceeded initial values.Distribution of ¹⁵N within the plant clearly showed that a significantamount of endogenous nitrogen in the roots was used by regrowingshoots. The greatest use of N reserves (about 80% of N incrementin the regrowing shoot) occurred during the first 10 d and thencompensated for the low N₂ fixation. The distribution of N derivedeither from fixation or from reserves of source organs (taproots and lateral roots) clearly showed that shoots are thestronger sink for nitrogen during regrowth. In non-defoliatedplants, the tap roots and stems were weak sinks for N from reserves.By contrast, relative distribution within the plant of N assimilatedin nodules was unaffected by defoliation treatment. Key words: Medicago sativa L., N₂ fixation, N remobilization, N₂ partitioning, regrowth     

The Effect of Nitrogen Source on Transport and Metabolism of Nitrogen in Fruiting Plants of Cowpea (Vigna unguiculata (L.) Walp.)

Nitrogen metabolism and transport were studied during reproductivedevelopment of cowpea (Vigna unguiculata (L.) Walp. cv. Vita3) under three contrasting nitrogen regimes: (1) nitrate suppliedcontinuously (plants non-nodulated), (2) symbiotic N₂ fixation(no combined nitrogen), (3) nitrogenstarvation post-anthesisof previously N₂-fixing plants. The last treatment involveddaily flushing of the root systems with 100% oxygen which suppressedpost-anthesis N₂-fixation by 76–79%, thereby making fruitgrowth almost entirely reliant upon mobilization of previouslyaccumulated nitrogen. The bulk of the xylem nitrogen (root bleedingsap or peduncle tracheal sap) of nitrate-fed plants was nitrateand amide, that of symbiotic and O₂-treated plants largely ureide.The composition of fruit cryopuncture phloem sap, however, wasclosely similar in all treatments, with most nitrogen as amidesand amino acids. The evidence suggested intense metabolic transferof root derived nitrate-N or ureide-N to amino acids by vegetativeplant parts prior to translocation to fruits. All tissues offruits showed patterns of development of enzymic activitiesconsistent with release of nitrogen from both ureides and amidesand re-assimilation of ammonia to form amino acids. Althoughthe levels of enzyme activities varied between treatments thedifferences could not be readily associated with individualpatterns of nitrogen transport in the treatments. Nitrogen sufficiencyin the NO₃-fed plants was marked by elevated vegetative biomassand low harvest indices for dry matter and nitrogen, while nitrogendeficiency of the O₂-treated plants was associated with seedabortion, small seed size and low seed nitrogen concentration,and efficient mobilization of nitrogen from vegetative partsto fruits. Key words: Nitrogen, Translocation, Cowpea     

氮素形态对小麦花后不同器官内源激素含量的影响

采用盆栽方法,研究了酰胺态氮、铵态氮和硝态氮对小麦(Triticum aestivum)花后根系、旗叶和籽粒内源激素IAA、GA₃、ABA和ZR含量的影响。结果表明,小麦不同器官的内源激素含量对3种氮素形态的响应不同。氮素形态调节籽粒灌浆是通过根系、旗叶和籽粒中内源激素的协同作用而实现的。酰胺态氮与硝态氮处理相比,小麦花后5~15 d,旗叶GA₃含量、籽粒IAA和ABA含量较高,籽粒灌浆速率(Grain-filling rate, GFR)较高;花后15~25 d,根系GA₃含量、旗叶IAA和GA₃含量、籽粒ABA含量较高,籽粒IAA含量较低,GFR较低。铵态氮与硝态氮处理相比,小麦花后5 d,籽粒ZR含量较高;花后15 d前后,籽粒IAA、ABA含量较低,GFR较低;花后20~25 d,根系ZR、GA₃含量较低,旗叶IAA、GA₃含量较低,ABA含量较高,籽粒ABA、GA₃含量较低,IAA含量较高,GFR较高。铵态氮比硝态氮处理的小麦籽粒粒重显著增加。铵态氮和酰胺态氮处理比硝态氮处理增产显著。建议在‘豫麦49’施肥时,使用铵态氮或酰胺态氮并配施硝化抑制剂。     

氮素添加对内蒙古羊草草原净氮矿化的影响

为了更好地了解天然草原氮素矿化对全球氮沉降背景和草原施肥管理模式的响应, 从2000年起对内蒙古典型草原羊草 (Leymu schinensis) 群落开展了长期的氮素添加实验, 分别设置对照 (N0), 添加5gNH4NO3·m-2 (N1.75) 、30gNH4NO3·m-2 (N10.5) 和80gNH4NO3·m-2 (N28) 4个氮素添加梯度。2002年, 从相邻的同时进行施肥的两个生态系统类型, 即1979年围封的样地A和1999年围封的样地B进行土壤取样, 在最佳温度 (25℃) 和最适土壤湿度 (即60%田间持水量) 下进行5周的室内培养, 并用阶段性淋溶方法研究了氮素添加对土壤氮矿化动态的影响。在A和B两个样地内, 氮素添加都显著改变了土壤的累积氮矿化量。最高氮素处理N28对应于最低的累积氮矿化量, 而低氮素处理N1.75使得累积氮矿化量达到最高。在N0和N1.75处理中, 硝态氮的含量高于铵态氮;在N28处理中, 却表现出相反的趋势。氮素添加显著降低了土壤的pH值, 但累积氮矿化量与土壤pH值、有机碳和全氮均没有显著的相关性。大多数氮素添加处理水平在样地A具有比样地B更高的土壤累积氮矿化量。     

Gaseous nitrogen emmissions from undisturbed terrestrial ecosystems: An assessment of their impacts on local and global nitrogen budgets

There is increasing interest in the importance of nitrogen gas emissions from natural (non-agricultural) ecosystems with respect to local as well as global nitrogen budgets and with respect to the effects of nitrogen oxides on atmospheric ozone levels and global warming. The volatile forms of nitrogen of common interest are ammonia (NH₃), nitrous oxide, (N₂O), dinitrogen (N₂), and NO_x (principally NO + NO₂). It is often difficult to attribute emissions of these compounds from soils to a single process because they are produced by a variety of common biogeochemical mechanisms. Although environmental conditions in the soil often appear to favor nitrogen gas emissions, the potential nitrogen gas emission rate from undisturbed ecosystems is rarely approached. The best estimates to date suggest that nitrogen gas emission rates from undisturbed ecosystems typically range from > 1 to perhaps 10 or 20 kg N ha^-1 yr^-1. Under certain conditions, however, emission rates may be much higher. For example, excreta from animals in grasslands may elevate ammonia volatilization up to 100 kg N ha^-1 yr^-1 depending on grazer density; tidal input of nutrients to coastal wetlands may support denitrification rates of several hundred kg N ha^-1 yr^-1 . Excepting such cases, gaseous nitrogen losses are probably a small component of the local nitrogen budget in most undisturbed ecosystems. However, emissions from undisturbed soils are an important component of the global source strengths for (N₂O + N₂), N₂O and NO_x (50%, 21%, and 10% respectively). Emission rates of N₂O from natural ecosystems are higher than assumed previously by perhaps 10 times. Large-scale disturbance may have a stimulatory effect on nitrogen emission rates which could have important effects on global nitrogen budgets. There is a need for more sophisticated methods to account for natural temporal and spatial variations of emissions rates, to more accurately and precisely assess their global source strengths.     

Laboratory incubations reveal potential responses of soil nitrogen cycling to changes in soil C and N availability in Mojave Desert soils exposed to elevated atmospheric CO2

Elevated atmospheric carbon dioxide (CO₂) has the potential to alter soil carbon (C) and nitrogen (N) cycling in arid ecosystems through changes in net primary productivity. However, an associated feedback exists because any sustained increases in plant productivity will depend upon the continued availability of soil N. We took soils from under the canopies of major shrubs, grasses, and plant interspaces in a Mojave Desert ecosystem exposed to elevated atmospheric CO₂ and incubated them in the laboratory with amendments of labile C and N to determine if elevated CO₂ altered the mechanistic controls of soil C and N on microbial N cycling. Net ammonification increased under shrubs exposed to elevated CO₂, while net nitrification decreased. Elevated CO₂ treatments exhibited greater fluxes of N₂O–N under Lycium spp., but not other microsites. The proportion of microbial/extractable organic N increased under shrubs exposed to elevated CO₂. Heterotrophic N₂‐fixation and C mineralization increased with C addition, while denitrification enzyme activity and N₂O–N fluxes increased when C and N were added in combination. Laboratory results demonstrated the potential for elevated CO₂ to affect soil N cycling under shrubs and supports the hypothesis that energy limited microbes may increase net inorganic N cycling rates as the amount of soil‐available C increases under elevated CO₂. The effect of CO₂ enrichment on N‐cycling processes is mediated by its effect on the plants, particularly shrubs. The potential for elevated atmospheric CO₂ to lead to accumulation of NH₄⁺ under shrubs and the subsequent volatilization of NH₃ may result in greater losses of N from this system, leading to changes in the form and amount of plant‐available inorganic N. This introduces the potential for a negative feedback mechanism that could act to constrain the degree to which plants can increase productivity in the face of elevated atmospheric CO₂.